ECOLOGICAL ASSESSMENT

STAGE 2, WEINAM CREEK PRIORITY DEVELOPMENT AREA

Prepared for Redland Investment Corporation

Biodiversity Assessment and Management Pty Ltd PO Box 1376 CLEVELAND 4163

Specialised ecological knowledge that reduces your risk

Document Control Sheet

File Number: 0397-008

Project Manager/s: Adrian Caneris

Client: Redland Investment Corporation

Project Title: Ecological Assessment – Stage 2 Weinam Creek

Project Author/s: Dr Jo Chambers and Shelley Trevaskis

Project Summary: Assess the terrestrial ecological values of lands within the Stage 2 development area for the Weinam Creek PDA.

Draft Preparation History:

Revision/ Checking History Track:

Version Date of Issue Checked by Issued by 0397-008 Draft A 26/06/2019 Paulette Jones Jo Chambers 0397-008 Version 0 13/1/2021 Paulette Jones Jo Chambers 0397-008 Version 1 22/1/2021 Jo Chambers

Document Distribution:

Destination Revision 1 Date 2 Date 3 Date 4 Date Dispatched Dispatched Dispatched Dispatched Client Copy 1 - 1 26/06/2019 0 13/1/2021 1 22/1/2021 digital Client Copy 1- hard copy PDF - server 1 26/06/2019 0 13/1/2021 1 22/1/2021 PDF – backup – 1 26/06/2019 0 13/1/2021 1 22/1/2021 archived Hard Copy - library

BAAM Pty Ltd File No. 0397-008 Version 1 NOTICE TO USERS OF THIS REPORT

Purpose of Report

Biodiversity Assessment and Management Pty Ltd has produced this report in its capacity as {consultants} for and on the request of Redland Investment Corporation (the "Client") for the sole purpose of providing an assessment of the ecological values of lands within the Stage 2 development area of the Weinam Creek PDA (the "Specified Purpose"). This information and any recommendations in this report are particular to the Specified Purpose and are based on facts, matters and circumstances particular to the subject matter of the report and the Specified Purpose at the time of production. This report is not to be used, nor is it suitable, for any purpose other than the Specified Purpose. Biodiversity Assessment and Management Pty Ltd disclaims all liability for any loss and/or damage whatsoever arising either directly or indirectly as a result of any application, use or reliance upon the report for any purpose other than the Specified Purpose.

This report has been produced solely for the benefit of the Client. Biodiversity Assessment and Management Pty Ltd does not accept that a duty of care is owed to any party other than the Client. This report is not to be used by any third party other than as authorised in writing by Biodiversity Assessment and Management Pty Ltd and any such use shall continue to be limited to the Specified Purpose. Further, Biodiversity Assessment and Management Pty Ltd does not make any warranty, express or implied, or assume any legal liability or responsibility for any third party's use in whole or in part of the report or application or use of any other information or process disclosed in this report and to the full extent allowed by law excludes liability in contract, tort or otherwise, for any loss or damage sustained by any person or body corporate arising from or in connection with the supply or use of the whole part of the report through any cause whatsoever.

Biodiversity Assessment and Management Pty Ltd has used information provided to it by the Client and governmental registers, databases, departments and agencies in the preparation of this report. Biodiversity Assessment and Management Pty Ltd does not know, nor does it have any reason to suspect, that the information provided to it was false, inaccurate, incomplete or misleading at the time of its receipt. This report is supplied on the basis that while Biodiversity Assessment and Management Pty Ltd believes all the information in it is deemed reliable at the time of publication, it does not warrant its accuracy or completeness and to the full extent allowed by law excludes liability in contract, tort or otherwise, for any loss or damage sustained by any person or body corporate arising from or in connection with the supply or use of the whole or any part of the information in this report through any cause whatsoever.

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Signed on behalf of Date: 13/01/2021 Biodiversity Assessment and Management Pty Ltd

Managing Director

BAAM Pty Ltd File No. 0397-008 Version 1 EXECUTIVE SUMMARY Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

EXECUTIVE SUMMARY

INTRODUCTION

This report has been prepared for Redland Investment Corporation to document the results of an ecological assessment over land proposed for the Stage 2 development of the Weinam Creek Priority Development Area (PDA) (the study area). The Stage 2 concept plan includes residential allotments and one super lot and a new roadway. The study area currently supports industrial buildings, car parks, mown/slashed areas and scattered stands of native trees.

The focus of this assessment was to identify (a) the terrestrial ecological values within and adjoining the Stage 2 study area, (b) potential impacts to the identified values from the proposed development, and (c) relevant Federal, State and Local government approvals and mitigation measures required to address the potential impacts.

METHODOLOGIES

The ecological assessment combined a desktop review to broadly characterise the currently recognised ecological values of the Study Site, with a field survey to verify the ecological values and enable an informed assessment of potential impacts from the proposed actions. The focus of the field survey was to verify State mapped ecological values, whilst searching for the presence of any conservation significant species and their preferred habitats, including animal breeding places.

GENERAL ECOLOGICAL VALUES

The Stage 2 area consists primarily of totally cleared lands that support vehicle parking and industrial buildings, with scattered trees. The southern and western boundaries of Stage 2 are fringed by Weinam Creek and associated riparian vegetation, some of which is tidally influenced.

SUMMARY OF ECOLOGICAL CONSTRAINTS AND LEGISLATIVE OBLIGATIONS

Commonwealth Considerations

The field survey has confirmed that Stage 2 contains no Threatened Ecological Communities (TECs). Vegetation bordering Stage 2 features species associated with TECs, however this vegetation did not meet criteria that identified it as the TEC.

No threatened flora or fauna species were recorded during the terrestrial survey. However, there is some potential for two threatened mammal (Koala and Grey-headed Flying-Fox) species to be present in or near the development area. The proposed development is unlikely to cause any significant impacts to threatened fauna species and a referral to the commonwealth is not deemed necessary.

One Weed of National Significance (WoNS) was recorded on site, this being Asparagus Fern Asparagus aethiopicus.

State Considerations

Matters of State Environmental Significance (MSES)

Vegetation associated with Weinam Creek immediately adjacent to the southern boundary of the Stage 2 development area are mapped as ‘Of Concern’ Regional Ecosystems (RE) 12.1.3/12.1.1 that were confirmed during the field assessment. This vegetation is also mapped as Essential Habitat for Eastern Curlew Numenius madagascariensis.

BAAM Pty Ltd File No. 0397-008 Version 1 EXECUTIVE SUMMARY Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

To the west of Stage 2, an area mapped by the state as Endangered RE12.5.2a, as well as Essential Habitat for Koala, was ground-truthed as RE12.3.5 (Least Concern). Although ground- truthed as a different RE, this vegetation still meets the Essential Habitat factors for Koala.

Approximately 42 m2 of mapped remnant vegetation will be cleared for the eastern stormwater outlet. For development for urban purposes in an urban area, the clearing of Of Concern vegetation is considered exempt clearing work, in accordance with the Planning Regulation 2017.

The field surveys did not record any State listed EVNT fauna species and, based on an assessment of habitats in the Study Area, no State listed EVNT flora or fauna species are considered likely to occur. Consequently, no significant impacts to protected wildlife habitat are expected as a result of the proposed actions.

The study area is not mapped as a wetland protection area, but Weinam Creek is mapped as a high ecological significance (HES) wetland under the Department of Environment and Science (DES) Referable Wetlands mapping. The clearing of approximately 42 m2 of vegetation on the northern boundary of the HES wetland for stormwater management is unlikely to cause any significant residual impacts to the ecological values of this wetland. Indirect impacts will be managed by appropriate management of stormwater. In addition, the proposed works includes the removal of native vegetation within the mapped 50 m buffer to this wetland. The loss of this vegetation is not likely to result in any significant impacts to the HES wetland.

The proposed works will not remove more than 50m2 of marine plants above tidal limits; therefore a significant residual impact on marine plants is unlikely.

State Government mapping shows that the project area is within a Koala Assessable Development Area. The Stage 2 development area is not mapped as supporting Core or Locally Refined Koala habitat. There no offset requirement under Schedule 11 of the Planning Regulation 2017 for the unavoidable clearing of Koala habitat trees in unmapped areas.

NC Act Obligations

No active animal breeding places were recorded during the field survey, although the Study Site supports potential animal breeding places for least concern species such as common birds. It is recommended the trees to be cleared and the inundation areas are inspected prior to clearing to determine if any native fauna are breeding and any necessary Species Management Program is obtained prior to works, as advised by the Department of Environment and Science (DES).

State Restricted Weeds

Two Category 3 restricted invasive weed species listed under the Queensland Biosecurity Act 2014 were recorded on site. In accordance with the Biosecurity Act 2014, Category 3 restricted invasive plants must not be distributed (i.e. released into the environment) unless the distribution or disposal is authorised in a regulation or under a permit. More generally, landowners are responsible for taking all reasonable and practical steps to minimise the risks associated with invasive plants under their control.

Matters of Local Environmental Significance

It is understood that, as the study area is a declared Priority Development Area, any development within the PDA does not have to comply with the Redland City Council Planning Scheme, but should have regard for any Council mapping of significant environmental values.

SUMMARY OF POTENTIAL IMPACTS AND MITIGATION MEASURES

BAAM Pty Ltd File No. 0397-008 Version 1 EXECUTIVE SUMMARY Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

With appropriate management, the conversion of the currently developed lands into a small residential development is not expected to cause any significant or prolonged impacts to the terrestrial ecological values of the Stage 2 area.

Appropriate management includes weed removal and buffer plantings along the western and southern edges of the proposed development to protect the retained vegetation from indirect impacts associated with the development. This would be achieved under the direction of an approved Rehabilitation/Restoration Plan.

Mitigation measures to prevent water quality to the health of higher valued habitats associated with Weinam Creek as a result of increased runoff of stormwater and/or pollutants entering the adjacent waterway, have been included within the finalised development plans.

All vegetation clearing will be undertaken under the guidance of a qualified fauna spotter/catcher.

BAAM Pty Ltd File No. 0397-008 Version 1 TERRESTRIAL ECOLOGICAL ASSESSMENT

STAGE 2 WEINAM CREEK PDA

Table of Contents

1.0 INTRODUCTION ...... 1 2.0 METHODOLOGY...... 1 2.1 Desktop...... 1 2.2 Terrestrial Field Survey...... 1 3.0 STUDY RESULTS AND LEGISLATIVE IMPLICATIONS...... 1 3.1 General Terrestrial Ecological Values ...... 1 3.1.1 Vegetation Communities...... 1 3.1.2 Fauna Habitats...... 5 3.1.3 Fauna Movement Opportunities...... 5 3.2 Matters of National Environmental Significance...... 5 3.2.1 Threatened Ecological Communities ...... 5 3.2.2 Threatened Flora Species...... 6 3.2.3 Threatened Fauna Species...... 7 3.2.4 Migratory Birds ...... 8 3.2.5 Ramsar Wetland ...... 8 3.2.6 Weeds of National Significance ...... 8 3.3 Matters of State Environmental Significance...... 9 3.3.1 Regulated Vegetation...... 9 3.3.2 Wetlands and Waterways ...... 9 3.3.3 Marine Plants ...... 10 3.3.4 South East Queensland Koala Planning Framework ...... 10 3.4 Matters Addressed Under the NC Act ...... 10 3.4.1 Flora ...... 10 3.4.2 Animal Breeding Places...... 10 3.5 Matters Addressed Under the Marine Parks Act ...... 12 3.6 Matters Addressed Under the Biosecurity Act...... 12 3.7 Weinam Creek Development Scheme and EDQ Guidelines ...... 12 3.8 Matters of Local Environmental Significance ...... 12 4.0 POTENTIAL IMPACTS AND MITIGATION RECOMMENDATIONS ...... 12 5.0 REFERENCES...... 13

Table of Figures Figure 1.1: Location of Study Area Figure 3.1: Vegetation Assessment Figure 3.2: Extent of Coastal Swamp Oak Figure 3.3: Extent of Coastal Saltmarsh Figure 3.4: Location of previous Flying-Fox Camp Figure 3.5: Trees >100mm recorded within the development area or within 10 m of the Stage 2 boundary

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Table of Appendices

Appendix 1: Stage 2 Concept Plan Appendix 2: Database Search Results Appendix 3 Matters of State Environmental Significance Mapping Appendix 4: Matters of Local Environmental Significance Mapping

Table of Abbreviations

BAAM Biodiversity Assessment and Management Pty Ltd DES Queensland Department of Environment and Science (formerly EHP) DMP Damage Mitigation Permit EHP Queensland Department of Environment and Heritage Protection (now DES) EPBC Act Commonwealth Environment Protection and Biodiversity Conservation Act 1999 EVNT Species listed as endangered, vulnerable or near threatened under the EPBC Act or NC Act MNES Matters of National Environmental Significance MSES Matters of State Environmental Significance NC Act Queensland Nature Conservation Act 1992 RE Regional Ecosystem SMP Species Management Program SRI Significant Residual Impact

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1.0 INTRODUCTION for conservation significant communities, habitats and flora and fauna species with This report has been prepared for Redland reference to the study area locality. Investment Corporation (RIC) to document the results of a terrestrial ecological assessment of 2.2 TERRESTRIAL FIELD SURVEY land proposed to be developed as part of the Stage 2 application within the Weinam Creek The terrestrial field survey was conducted Priority Development Area (PDA). during daylight hours on 14 June 2019 during warm, fine conditions. The survey included The Weinam Creek PDA Stage 2 application identifying all trees ≥100 mm DBH within and encompasses Lot 6 RP178363, Lot 1 RP90590 immediately adjacent to the proposed and Lot 143 SL843, located at 22 Meissner development. Street, Redland Bay (study area) (Figure 1.1). A particular focus of the field surveys was to The Weinam Creek Development Scheme (DSIP identify the presence/absence conservation 2014) guides the planning, execution, promotion, significant flora and fauna species and their coordination and control of the development of habitats. This included inspection of vegetation land in the Weinam Creek PDA. The for flora and fauna species or animal breeding development scheme supersedes the interim places, searching the ground layer for animal land use plan which no longer has effect. signs (scats, burrows) and appraising the vegetation and surrounding land uses to provide The Development Application and any approval an overall assessment of the habitat values for conditions of the Weinam Creek PDA Stage 2 conservation significant flora and fauna. application will be managed by the Minister for Economic Development Queensland (MEDQ) in partnership with Redland City Council. 3.0 STUDY RESULTS AND LEGISLATIVE IMPLICATIONS All development applications within the Weinam Creek PDA will now be assessed against the 3.1 GENERAL TERRESTRIAL ECOLOGICAL Weinam Creek Development Scheme and VALUES sustainable resource use within the PDA will also be guided by PDA guideline no. 14 (DILGP 3.1.1 Vegetation Communities 2015). The Stage 2 area is primarily cleared land that The Stage 2 concept plan (Appendix 1) includes supports vehicle parking and industrial buildings, residential allotments, one super lot and a new with some patches of vegetation present on the roadway. The study area currently supports boundaries and in the northern portion of the industrial buildings, car parks, mown/slashed study area. The southern and western areas and scattered stands of native trees. boundaries of Stage 2 are fringed by Weinam Creek and associated riparian vegetation, some The focus of this assessment is to identify (a) of which is tidally influenced (Figure 1.1). the terrestrial ecological values within and adjoining the Stage 2 study area, (b) potential The site assessment referred to the definitions impacts to the identified values from the given for significant vegetation as defined by the proposed development, and (c) relevant Weinam Creek Priority Development Area Federal, State and Local government approvals Development Scheme in which significant and mitigation measures required to address the vegetation means all vegetation, except those potential impacts. listed as pest vegetation by State or local government, that is significant in its:

2.0 METHODOLOGY  ecological value at local, state or national levels including vegetation mapped as 2.1 DESKTOP endangered remnant vegetation on the regional ecosystem maps prepared under The desktop review comprised a search of the Vegetation Management Act 1999 or online ecological mapping and databases and vegetation mapped as a Matter of State an analysis of existing information, including Environmental Significance on the DSDIP previous reporting for the for the PDA State Planning Policy Interactive Mapping application (BAAM & frc environmental 2013) System

BAAM Pty Ltd Page 1 File No. 0397-008 Version 1 N 6945400 N 6945600 N 6944400 N 6944600 N 6944800 N 6945000 N 6945200 Aerial Photo:Nearmap-December 2017 LEGEND c BiodiversityAssessmentandManagement PtyLtd.Whileeverycareistakentoensuretheaccuracy ofthisdata,BiodiversityAssessmentandManagementmakes norepresentationsorwarrantiesaboutitsaccuracy,reliability, completenessorsuitabilityforanyparticularpurposeand disclaims allresponsibilityand liability(includingwithoutlimitationinnegligence)forall expenses, losses,damages(includingindirectconsequentialdamage) andcostswhichmightbeincurredasaresultofthedatabeing inaccurateorincompleteinanywayandforreason. 0 Scale 1:5000 50 PDA Boundary Stage 2Boundary 100 150m

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 Contribution to the preservation of natural the height, canopy cover and dominant species landforms present in each stratum of a vegetation community and inform the applicable remnant  Contribution to the character of the status and regional ecosystem (RE) type. landscape  Cultural or historical value Table 3.1 provides a description and  Amenity value to the general public. representative photographs of vegetation communities sampled within and adjacent to the Stage 2 area. Table 3.2 with reference to Quaternary site data was recorded at Figure 3.1 lists all weed species recorded representative locations (refer Figure 3.1) in within and/or adjacent to the Stage 2 study accordance with the methodology prescribed in area. Neldner et al. (2019). Quaternary sites measure

Table 3.1. Description of vegetation recorded at assessment sites. Site Habitat description Representative photo Q1 Regional Ecosystem: RE12.5.2a with non-remnant fringe. Ground-truthed as RE12.3.5. Canopy (T1): Dense. Height range 12-15m; median height 14m. Dominant species: Melaleuca quinquenervia. Associated species: Casuarina glauca, (edge only), Glochidion sumatranum, Archontophoenix alexandrae. Sub-canopy (T2): Dense (edge) to Sparse (interior). Height range 6-8m; median height 7m. Co-dominant species: Archontophoenix alexandrae (interior), Macaranga tanarius, Melaleuca quinquenervia, Casuarina glauca. Groundcover: Dense Height range 0.5-1.5m; median height 0.5m. Co-dominant species: Blechnum indicum, Phragmites Q1 Adjacent vegetation on south western australis boundary Associated species: Acrostichum speciosum, Parsonsia straminea.

Q1 interior vegetation Q2 Regional Ecosystem: RE12.1.3/RE12.1.1. Ground-truthed as correct (RE12.1.1 applies to edge vegetation). Canopy (T1): Dense. Height range 10-14m; median height 14m. Dominant species: Casuarina glauca. Sub-canopy (T2): Dense. Height range 6-8m; median height 6m. Dominant species: Macaranga tanarius (edge) Casuarina glauca (interior). Associated species: Neonotonia wightii* Groundcover: Sparse Height range 0.1-0.4m; median height 0.2m. Dominant species: Neonotonia wightii* Associated species: Megathyrsus maximus*, Chloris gayana*, Phragmites australis, Parsonsia straminea. Q2 Adjacent vegetation on southern boundary

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Site Habitat description Representative photo

Q interior vegetation Q3 Regional Ecosystem: RE12.1.3/RE12.1.1. Ground-truthed as correct (RE12.1.1 applies to edge vegetation assessed). Canopy (T1): Dense. Height range 7-10m; median height 9m. Dominant species: Casuarina glauca. Sub-canopy (T2): Very sparse. Height range 2-4m; median height 3m. Dominant species: Casuarina glauca Associated species: Neonotonia wightii*, Cupaniopsis anacardioides. Shrub (S1): Very sparse. Height range 1-2m; median height 1m. Dominant species: Senna pendula* Groundcover: Mid-dense Height range 0.1-0.3m; median height 0.2m. Dominant species: Ottochloa gracillima Q3 Vegetation on northern bank of Weinam Associated species: Stephania japonica, Neonotonia wightii*. Creek Q4 Regional Ecosystem: non-remnant Canopy (T1): Dense. Height range 6-8m; median height 8m. Dominant species: Casuarina glauca. Shrub (S1): Very sparse. Height range 1-2m; median height 2m. Dominant species: Casuarina glauca Associated species: Lophostemon confertus Groundcover: Dense Height range 0.5-2m; median height 1.5m. Dominant species: Phragmites australis.

Q4 Vegetation in ephemeral drainage line that connects with Weinam creek Q5 Regional Ecosystem: non-remnant Canopy (T1): Dense. Height range 6-9m; median height 9m. Co-dominant species: Casuarina glauca, Melaleuca quinquenervia, Grevillea robusta Associated species: Parsonsia straminea Sub-canopy (T2): Very sparse. Height range 5-6m; median height 5m. Dominant species: Casuarina glauca Groundcover: Dense Height range 1-2m; median height 2m. Dominant species: Phragmites australis.

Q5 Vegetation in ephemeral drainage line that connects with Weinam creek

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Site Habitat description Representative photo Q6 Regional Ecosystem: non-remnant. Canopy (T1): Mid-dense. Height range 15-17m; median height 17m. Dominant species: Eucalyptus tereticornis. Associated species: Eucalyptus resinifera. Sub-canopy (T2): Mid-dense Height range 6-10m; median height 8m. Dominant species: Melaleuca quinquenervia Associated species: Glochidion sumatranum, Grevillea robusta, Eucalyptus tereticornis. Shrub (S1): Mid-dense. Height range 1-2m; median height 2m. Co-dominant species: Casuarina glauca Associated species: Senna pendula*, Schinus terebinthifolius*, Schefflera actinophylla*, Melicope elleryana, Q6 Vegetation adjacent to the north eastern Grevillea robusta. boundary of the study area Groundcover: Mid-dense Height range 0.1-0.5m; median height 0.2m. Co-dominant species: Pteridium esculentum, Phragmites australis, Megathyrsus maximus*, Cyperus polystachyos. Q7 Regional Ecosystem: non-remnant Canopy (T1): Dense. Height range 5-7m; median height 6m. Dominant species: Casuarina glauca. Shrub (S1): Very sparse. Height range 0.5-1.5m; median height 1m. Dominant species: Casuarina glauca Groundcover: nil.

Q7 Vegetation on the north-eastern bank of Weinam Creek Q8 Regional Ecosystem: non-remnant Canopy (T1): Dense. Height range 5-9m; median height 9m. Dominant species: Casuarina glauca. Associated species: Parsonsia straminea Shrub (S1): Very sparse. Height range 0.5-1.5m; median height 1m. Dominant species: Casuarina glauca Groundcover: Very sparse Height range 0.1-0.5m; median height 0.5m. Dominant species: Megathyrsus maximus*.

Q8 Vegetation on the northern bank of Creek, adjacent to eastern boundary of study area Q9 Regional Ecosystem: non-remnant. Canopy (T1): Mid-dense. Height range 11-18m; median height 18m. Dominant species: Eucalyptus tereticornis. Sub-canopy (T2): Dense Height range 6-9m; median height 7m. Dominant species: Acacia disparrima Associated species: Grevillea robusta. Shrub (S1): Very sparse. Height range 1-2m; median height 1m. Dominant species: Grevillea robusta Associated species: Schinus terebinthifolius*, Macaranga tanarius. Groundcover: Sparse Height range 0.1-0.4m; median height 0.3m. Q9 Vegetation adjacent to carpark near Co-dominant species: Megathyrsus maximus*, Rivina Meissner Street boundary humilis*, Passiflora suberosa*.

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PDA Boundary Weinam Stage 2 Boundary 12.3.5 Recommended 50m Buffer Quaternary Site Weed Record Regional Ecosystems DNRM Version 8 2010 12.5.2a Endangered; Dominant Of Concern; Sub-dominant Least Concern Client Project Essential Habitat Ecological Assessment Scale 1 : 1500 Redland Investment Corporation Stage 2 Weinam Creek PDA 0 20 50m Design BAAM 13.01.2021 Title FIGURE Drawn MP 13.01.2021 Vegetation Assessment Aerial Photo: Nearmap - November 2021 Scale 1:1500 # 0397-008 3.1 Cad File BAAM_Weinam Ck10.dwg NTP 145 E 530400 E 530500 E 530300 c Biodiversity Assessment and Management Pty Ltd. While every care is taken to ensure the accuracy of this data, Biodiversity Assessment and Management makes no representations or warranties about its accuracy, reliability, completeness or suitability for any particular purpose and disclaims all responsibility and all liability (including without limitation liability in negligence) for all expenses, losses, damages (including indirect consequential damage) and costs which might be incurred as a result of the data being inaccurate or incomplete in any way and for any reason. Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

Table 3.2. Weed species recorded within an/or adjacent to the study area. Weed Record Site State Restricted Species WONS (Figure 3.1) Weed W1 Broad-leaved Pepper Tree Schinus terebinthifolius ** Y W2 Guinea Grass Megathyrsus maximus Giant Devils Fig Solanum chrysotrichum White Glycine Neonotonia wightii W3 Asparagus Fern Asparagus aethiopicus YY Ochna Ochna serrulata Easter Cassia Senna pendula W4 Asparagus Fern Asparagus aethiopicus YY W5 Asparagus Fern Asparagus aethiopicus YY Ochna Ochna serrulata Callisia Callisia fragrans

3.1.2 Fauna Habitats of Meissner Street to the north and Weinam Creek to the south and west. Due to existing and past land uses, much of the study area supports limited habitat values for The proposed development will not significantly native fauna species. Highest habitat values alter current fauna movement opportunities. are associated with mature and regrowth vegetation within the north-western corner of 3.2 MATTERS OF NATIONAL the proposed Super Lot (refer Figure 3.1). ENVIRONMENTAL SIGNIFICANCE Floristic diversity as well as thick leaf litter and ground debris at this location provides feeding 3.2.1 Threatened Ecological Communities and refuge habitats for locally common native and non-native birds, reptiles and mammals. The EPBC Protected Matters Search (Attachment 2) indicates that the following The wetland immediately adjoining the Stage 2 three EPBC Act Threatened Ecological study to the south area holds high value fauna Communities (TECs) could potentially occur habitats. within the study area:

Fauna recorded within the Stage 2 study area  Coastal Swamp Oak (Casuarina glauca) during the site assessment included locally Forest of New South Wales and South common bird species such as Australian East Queensland (Endangered); Magpie Cracticus tibicen, Noisy Miner Manorina melanocephala, Rainbow Lorikeet  Lowland Rainforest of Subtropical Trichoglossus moluccanus and Grey Fantail Australia (Critically Endangered) and Rhipidura albiscapa. The fauna assemblage  Subtropical and Temperate Coastal present is typical of urbanised areas. Saltmarsh (Vulnerable).

A Brahminy Kite Haliastur indus was observed Coastal Swamp Oak in a standing dead tree near the creek channel to the south of the study area. Two distinct and separate narrow strips of Swamp Oak Casuarina glauca-dominated 3.1.3 Fauna Movement Opportunities vegetation were recorded during the field survey, fringing mangrove vegetation Fauna movement opportunities are constrained associated with Weinam Creek (Figure 3.2). within the study area by the presence of buildings and cleared car park areas and is The southern patch is located within the Stage currently expected to be restricted to vegetation 1 project precinct. The northern patch directly in the eastern portions of the site and along the adjoins the southern boundary of Stage 2 and southern and western boundaries. Movement may be subject to indirect impacts (e.g. light, opportunities for non-vagile species outside of hydrological changes) associated with the the study area are constrained by the presence proposed development.

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Figure 3.3. Pink polygons showing the full extent of Salt Couch Sporobolus virginicus patches recorded adjacent to Stage 2.

In accordance with the Approved Conservation Advice for Subtropical and Temperate Coastal Figure 3.2. White polygons showing the full Saltmarsh (DSEWPaC 2013), the listed extent of the Swamp Oak Casuarina glauca ecological community is limited to areas and communities associated with Weinam Creek. patches of coastal saltmarsh that meet the Key Diagnostic Characteristics and Condition In accordance with the Approved Conservation Thresholds as published in the Listing Advice. Advice for the Coastal Swamp Oak (Casuarina glauca) Forest of New South Wales and South The patches of Salt Couch recorded adjacent to East Queensland TEC (DoEE 2018), the Stage 2 southern boundary all occur under a ecological community must meet both the Key dense (near 100%) canopy cover of Casuarina Diagnostic Characteristics and at least the glauca (Photo 1). A Key Diagnostic Criteria for minimum Condition Threshold as published in this TEC requires tree cover to be less than 50%. the Listing Advice.

It is noted that the Condition Threshold for this community requires any patch to be at least 0.5ha in area to meet TEC status.

The northern patch is 0.42 ha in area and the southern patch is 0.34 ha in area. As such, they do not meet the minimum area requirement and do not meet the criteria for the TEC.

Lowland Rainforest

No vegetation communities with species indicative of the Lowland Rainforest of Subtropical Australia’’ TEC were identified Photo 1: Salt Couch under canopy of Casuarina glauca during the field survey, confirming that this TEC does not occur within or adjacent to the Stage 2 The small areas of Salt Couch recorded and development area. described above do not meet the thresholds for the Subtropical and Temperate Coastal Subtropical and Temperate Coastal Saltmarsh TEC. Saltmarsh 3.2.2 Threatened Flora Species Four small areas (0.007; 0.003; 0.001 and 0.009 ha) of Salt Couch Sporobolus virginicus A review of the nationally listed flora species were recorded within tidally influenced returned by the EPBC Protected Matters vegetation along Weinam Creek, south of the database search for the site and a 2km radius Stage 2 boundary (Figure 3.3). (Appendix 2) determined that most listed

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species are associated with rainforest habitats that were not present within or adjacent to the study area.

Of the species returned by the search, one (Hairy-joint Grass Arthraxon hispidus) was assessed as potentially present in vegetation bordering Stage 2. This species may be associated with freshwater springs on coastal foreshore dunes, in shaded small gullies, on creek banks, and on sandy alluvium in creek beds in open forests (DEWHA, 2008). Vegetation to the west of the Stage 2 development area, which featured a Broad- leaved Paperbark Melaleuca quinquenervia dominated wetland was considered the only potential habitat for the species. Figure 3.4 Purple polygons show extent of previous Flying-fox camp. Assessment of vegetation on the perimeter of As the proposed Stage 2 development does this wetland area did not record the species and there are no state records from the locality not include any direct or significant indirect (Wildlife online, Appendix 2). Accordingly, this impacts to the previously recorded Flying-fox species is considered unlikely to occur. roost location, there will be no significant impacts to Grey-headed Flying-fox from the proposal. 3.2.3 Threatened Fauna Species Grey-headed Flying-fox is well known to The EPBC Protected Matters Search tolerate urban uses in proximity to their roosting (Appendix 2) returned a number of threatened areas; however, if the camp was to re- fauna species that may potentially occur within establish, future residents of the Stage 2 area the Stage 2 development area. may object to the noise and odour associated with a flying-fox roost. No threatened r fauna species were recorded during the terrestrial survey. However, there is The Weinman Creek PDA is within the some potential for two threatened mammals to designated Urban Flying-Fox Management be present in or near the development area. Area. Under the Nature Conservation Act 1992, the State Government provides for flying-fox Grey-headed Flying- Fox Pteropus roost management to allow local governments poliocephalus to make their own decisions about how to best manage individual flying-fox roosts on Council A Flying-fox roost has previously been controlled lands in designated Urban Flying- recorded in the southern portions of Weinam Fox Areas. Creek, outside of the Stage 2 development area (Figure 3.4); the roost is known to have The legislation authorises local government to been used seasonally by up to two thousand act on these decisions without the need for a Grey-headed Flying-fox for mating, birthing and permit under the Nature Conservation Act 1992 as a maternity camp (BAAM & frc and therefore any ongoing management of environmental 2013). No Flying-fox were flying-foxes, should they recolonise the area, present at the time of the site assessments will be under the Redland City Council conducted and none have been recorded at jurisdiction. Redland City Council has released this roost since May 2015 (DoE 2019a). As this a Statement of Management Intent to articulate is a seasonal roost (detailed in BAAM 2013), the approach that will be taken in the and the species is known to disperse in management of flying-fox roosts in designated response to flowering/fruiting events, it is Urban Flying-Fox Management Areas in the possible that the roost will re-establish in the Redlands. known roosting location or nearby vegetated areas in the future. Where Council owned or managed land is used as a roost site by flying-foxes, Council will:

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 Not disperse flying-foxes or destroy flying- development should ensure ongoing provision fox roost sites; is made to facilitate safe Koala movement opportunities within the landscape.  Continue to reinforce education to the community; 3.2.4 Migratory Birds  Continue to revegetate previously used roosts in areas of less conflict Identify sites Database searches (Appendix 2) indicate the for enhancement as potential future roost potential presence of EPBC Act listed migratory sites; species. A number of these species have  Continue to monitor and map our roost potential to be seasonal visitors to the adjoining sites in partnership with Department of wetland area and could occasion the study Environment and Heritage Protection and area. volunteers; However, the study area would not support an  Continue to liaise closely with other local ecologically significant proportion of habitat for Councils, researchers and Department of migratory species, and all potentially occurring Environment and Heritage Protection migratory species are common, widely- officers; distributed species that are neither known to be  Advocate on behalf of the community to declining nor at the limit of their range within State Government agencies to assist with the local area. flying-fox management; and

 Ensure that Council management for flying- Therefore, any future development of the study foxes is undertaken in accordance with the area is unlikely to have a significant impact on Code of Practice – Ecologically sustainable migratory species, and it is considered that a management of flying-fox roost’; Procedure referral to the Commonwealth is not warranted 3070-001-002 Working around Flying-foxes in relation to potential impacts upon migratory and Roost Sites and any other legislative species. requirements. 3.2.5 Ramsar Wetland Koala Phascolarctos cinereus The Stage 2 area is adjacent to the Moreton Bay No Koala or evidence of their utilisation of the Wetland of International Importance, listed under study area was observed during the field the Convention on Wetlands of International survey. The north-eastern corner of the study Importance 1971 (Ramsar Convention). area supports a number of Forest Red Gum Eucalyptus tereticornis, which is a known Koala No works are proposed within the Ramsar food tree. This is the only location where Koala wetland in Stage 2. However management food trees were present, although Koala habitat measures must be enacted to ensure the trees in the form of Melaleuca quinquenervia proposed development will not result in a were scattered throughout the surrounding significant impact on water quality and the habitats. The resident of the house near the aquatic environment within the receiving waters north-eastern boundary of the study area of Moreton Bay. indicated that while Koalas used to be present in the large Forest Red Gum in front of his Appropriate controls during construction and property, no Koalas have been observed in the operational phases are required. local area for a number of years. 3.2.6 Weeds of National Significance As there was no evidence of Koala, a paucity of Koala food trees in the local area and the One Weed of National Significance (WONS) surrounding land uses include high traffic was recorded on site, this being Lantana roadways and rapidly expanding residential Asparagus Fern Asparagus aethiopicus. developments, it is considered unlikely that Koala would be present within the study area. Minor occurrences of this species were recorded at locations W3, W4 and W5 shown Although the species is generally unexpected, on Figure 3.1. Landholders or managers are based on records within 2km of the study area responsible for managing WONS. Koalas do have potential to occur within the Weinman Creek PDA. Overall, the site

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3.3 MATTERS OF STATE ENVIRONMENTAL Conservation Act 1992 (NC Act) have been SIGNIFICANCE recorded within 2 km of the study area since 1980 and based on the disturbed nature of the State Planning Policy mapping shows the existing vegetation within and immediately entire study area falls within the Coastal adjacent to Stage 2, no threatened flora Management District. Consequently, subject to species are expected to occur. any exemptions that apply, the proposed works may need to address State Code 8: Coastal The Wildlife Online database (Appendix 2) development and tidal works, which requires lists three records for Eastern Curlew the significance of impacts to all MSES to be Numenius madagascariensis, one for Dugong assessed, with the exception of wetlands or Dugon dugon and 269 records for Koala within watercourses in high ecological value waters. a 2 km buffer of the study area since 1980. The terrestrial MSES mapped and/or recorded within or in close proximity to the study area The Stage 2 development area does not are discussed in the following sections. support habitats for Eastern Curlew or Dugong. However appropriate management of 3.3.1 Regulated Vegetation stormwater runoff must be included in the final development plans for the site to ensure no Vegetation associated with Weinam Creek indirect impacts to these species habitats in immediately adjacent to the southern boundary Moreton Bay. of the Stage 2 development area is mapped as ‘Of Concern’ Regional Ecosystems (RE) The north-eastern portion of the Stage 2 12.1.3/12.1.1 (Appendix 3). This was development area supports a number of confirmed as correct during the field potential food trees for Koala. However, there assessment. This vegetation is also mapped as was no evidence (scats or scratches) of Koala Essential Habitat for Eastern Curlew Numenius utilisation of the study area and based on the madagascariensis. Eastern Curlew is not paucity of Koala habitat present, it is expected to occur within the study area. considered unlikely that Koala would utilise the study area. Koala is discussed further in To the west of Stage 2, an area of vegetation is Section 3.3.5. mapped by the state as Endangered RE12.5.2a (Corymbia intermedia, Eucalyptus Consequently, with appropriate protection of tereticornis open forest on remnant Tertiary off-site water quality, there are no predicted surfaces, usually near coast), and is identified significant impacts to threatened flora or fauna as comprising Essential Habitat for Koala. This species likely to result from the proposed vegetation was ground-truthed as RE12.3.5, actions. described as Melaleuca quinquenervia open forest on coastal alluvium (Least Concern). 3.3.3 Wetlands and Waterways Although ground-truthed as a different RE, this vegetation still meets the Essential Habitat The study area is not mapped as a wetland factors for Koala. protection area; however, the area of Weinam Creek south of the Stage 2 development area Approximately 42 m2 of mapped remnant is mapped as a high ecological significance vegetation will be cleared for the eastern (HES) wetland under the Department of stormwater outlet pipe. However, for Environment and Science (DES) Referable development for urban purposes in an urban Wetlands mapping (Attachment 3). area, the clearing of ‘Of Concern’ vegetation and Essential Habitat is considered exempt There will be a slight incursion for the eastern clearing work, in accordance with the Planning stormwater outlet into the mapped HES Regulation 2017; therefore there are no wetland as part of the Stage 2 development constraints under the VM Act for any clearing of (Figure 3.5). mapped ‘of concern’ vegetation. Under PDA guideline no. 14 (EDQ 2015), a 3.3.2 Threatened Species minimum buffer of 50 m between the proposed development and the HES wetland is The Wildlife Online database return (Appendix recommended, although encroachment into the 2) indicates that no flora species listed as 50 m HES buffer is not prohibited. Much of the Endangered, Vulnerable or Near Threatened Stage 2 development footprint falls within the (EVNT) under the Queensland Nature 50 m buffer. However, vegetation and hence

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ecological values within the buffer are restricted The clearing of less than 42 m2 of marine plants to rows of planted trees within and bordering (Casuarina glauca), which are located on the the existing car park areas and the patch of northern boundary of the marine influenced bushland within the Super Lot (Figure 3.5, area, for the eastern stormwater outlet pipe is Appendix 6). unlikely to result in a significant residual impact.

Approximately 42 m2 of vegetation within the There is more than 50m2 of marine plants HES wetland will require clearing for a above tidal limits within the Super Lot. Any stormwater outlet pipe. The loss of this vegetation clearing proposed in this location vegetation is not likely to result in any would need to address the requirements of the significant impacts to the HES wetland. Fisheries Act 1994. Appropriate management of stormwater runoff has been included in the Stage 2 development 3.3.5 South East Queensland Koala plans to ensure changes to the natural Planning Framework hydrological regime and/or water quality that could impact on the HES wetland do not occur State Government mapping shows that the as a result of construction and operation. project area is within a Koala Assessable Development Area. The Stage 2 development Weed removal and supplementary restoration area is not mapped as supporting Core or plantings along the southern and western Locally Refined Koala habitat (Attachment 3). edges of the Stage 2 development area will enhance the existing ecological values of There no offset requirement under Schedule 11 vegetation within the mapped HES wetland and of the Planning Regulation 2017 for the will assist in buffering the HES wetland from unavoidable clearing of Koala habitat trees in any adverse impacts as a result of the unmapped areas. proposed development. 3.4 MATTERS ADDRESSED UNDER THE NC 3.3.4 Marine Plants ACT

Marine plants, in the form of Casuarina glauca 3.4.1 Flora were recorded in the central portions of the Super Lot. The Queensland Fisheries Act 1994 The study area is not within a high risk area on defines ‘marine plants’ as follows: the protected flora trigger map. A search of the DES Wildlife Online database (Appendix 2) no “Marine plant includes the following: EVNT flora species listed under the NC Act has (a) a plant (a tidal plant) that usually grows on, been previously recorded within 2 km of the or adjacent to, tidal land, whether it is living, study area since 1980. dead, standing or fallen; No threatened flora species were detected (b) material of a tidal plant, or other plant within the search area during the field survey. material on tidal land; Consequently, no direct or indirect impacts on (c) a plant, or material of a plant, prescribed protected plant species are expected to occur under a regulation or management plan to be a and no mitigation measures are considered marine plant. necessary.

Marine plant does not include a plant that is a 3.4.2 Animal Breeding Places declared pest under the Land Protection (Pest and Stock Route Management) Act 2002”. No active animal breeding places were recorded during the field survey, although the The Significant Residual Impact Guideline study area supports potential animal breeding states an action is LIKELY to have a Significant places for least concern species such as Residual Impact on marine plants if more than nesting birds. All vegetation to be removed 50m2 of marine plants above tidal limits will be should be inspected prior to clearing to permanently removed as a result of the project, determine if any active animal breeding places and onsite rehabilitation or restoration will not are present and any necessary Species result in an equal or larger area of marine Management Program (SMP) is obtained prior plants, providing equal or better fisheries to works, as advised by DES. values, within 5 years of clearing.

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LEGEND PDA Boundary Stage 2 Boundary HES Wetland 50m Buffer to HES Wetland Clearing areas for Stormwater Outlets 7UHHV•PP'%+ Client Project Scale 1 : 1500 Ecological Assessment Redland Investment Corporation Stage 2 Weinam Creek PDA 0 20 50m Design BAAM 13.01.2021 Title FIGURE Drawn MP 13.01.2021 Aerial Photo: Nearmap - November 2021 7UHHV•PP'%+ Scale 1:1500 # 0397-008 3.5 Cad File BAAM_Weinam Ck10.dwg NTP 145 E 530400 E 530500 E 530300 c Biodiversity Assessment and Management Pty Ltd. While every care is taken to ensure the accuracy of this data, Biodiversity Assessment and Management makes no representations or warranties about its accuracy, reliability, completeness or suitability for any particular purpose and disclaims all responsibility and all liability (including without limitation liability in negligence) for all expenses, losses, damages (including indirect consequential damage) and costs which might be incurred as a result of the data being inaccurate or incomplete in any way and for any reason. Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

3.5 MATTERS ADDRESSED UNDER THE 3.8 MATTERS OF LOCAL ENVIRONMENTAL MARINE PARKS ACT SIGNIFICANCE

The north-eastern point of the Stage 2 It is understood that, as the study area is a development area meets the boundary of a declared Priority Development Area, any General Use Zone of the Moreton Bay Marine development within the PDA is not specifically Park. The objectives of General Use Zones are required to comply with the Redland City to provide for the conservation of the areas of Council Planning Scheme, but should have the marine park within the zone, and to provide regard for any Council mapping of significant opportunities for reasonable use within this environmental values. constraint. Under Redlands City Plan Version 2 a small Management measures must be enacted to area of vegetation within the Super Lot is ensure the proposed development will not mapped as ‘urban non Koala habitat’, and result in a significant impact on water quality vegetation within the new access road is and the aquatic environment within the mapped as ‘urban Koala habitat trees’ receiving waters of Moreton Bay. (Appendix 4).

Appropriate controls during construction and Vegetation adjacent to the southern boundary operational phases are required. of the study area is mapped as RE Remnant Koala habitat. However, this vegetation is 3.6 MATTERS ADDRESSED UNDER THE dominated by Casuarina glauca which is not a BIOSECURITY ACT Koala habitat tree species, with only a very sparse scattering of Koala habitat trees, i.e. Two restricted invasive weed species listed as Melaleuca quinquenervia present. It is Category 3 restricted invasive plants under the therefore considered that this mapping overlay Queensland Biosecurity Act 2014 were is inaccurate. recorded in vegetation immediately adjacent to an/or within Stage 2, these being: Vegetation adjacent to the western boundary of the Study Site is dominated by Melaleuca quinquenervia; a species that is listed as a  Broad-leaved Pepper Tree Schinus terebinthifolius (Site W1, Figure 3.1); and Koala habitat tree, although is not recognised as a Koala food tree (AKF 2014).  Asparagus Fern Asparagus aethiopicus (Sites W3, W4, W5, Figure 3.1). It is recommended that restoration activities are conducted within adjacent native vegetation, In accordance with the Biosecurity Act 2014, including weed removal and buffer plantings. Category 3 restricted invasive plants must not be distributed (i.e. released into the environment) unless the distribution or disposal 4.0 POTENTIAL IMPACTS AND is authorised in a regulation or under a permit. MITIGATION More generally, landowners are responsible for RECOMMENDATIONS taking all reasonable and practical steps to minimise the risks associated with invasive plants under their control. With appropriate management, the conversion of the currently developed lands 3.7 WEINAM CREEK DEVELOPMENT SCHEME into a small residential development is not AND EDQ GUIDELINES expected to cause any significant or prolonged impacts to the terrestrial ecological The proposed development aligns with the values of the Stage 2 area. Precinct 3 provisions of the Weinam Creek PDA Development Scheme. Appropriate management includes weed removal and buffer plantings along the Environmental values and sustainable resource western and southern edges of the proposed use are guided by PDA Guideline no. 14 development to protect the retained (DILGP 2015). This Ecological Assessment has vegetation from indirect impacts associated identified ecological process and natural with the development. This would be systems in accordance with the guideline achieved under the direction of an approved strategies. Rehabilitation/Restoration Plan.

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Mitigation measures to prevent water quality have been included within the finalised to the health of higher valued habitats development plans. associated with Weinam Creek as a result of increased runoff of stormwater and/or pollutants entering the adjacent waterway,

5.0 REFERENCES Environment and Energy. Available from:http://www.environment.gov.au/bi Australian Koala Foundation (AKF) (2014). odiversity/threatened/communities/pu National Koala Tree Planting List. bs/141-conservation-advice.pdf. In effect under the EPBC Act from 20-Mar- 2018.. BAAM and frc environmental (2013). Expert advice in ecology (marine and terrestrial) and coastal processes for input to the DoE (2019a). National Flying-dox Monitoring preparation of a structure plan and Viewer. development scheme for Toondah http://www.environment.gov.au/webgis- Harbour and Weinam Creek Priority framework/apps/ffc-wide/ffc-wide.jsf Development Areas (PDAs). Report Accessed June 2019. prepared for Redland City Council. Department of Infrastructure, Local Department of the Environment, Water, Government and Planning (DILGP) Heritage and the Arts (2008). Approved (2015). Environmental values and Conservation Advice for Arthraxon sustainable resource use PDA guideline hispidus (Hairy-joint Grass). Canberra: no. 14. Department of the Environment, Water, Heritage and the Arts. Available from: DSIP (2014). Weinam Creek Priority http://www.environment.gov.au/biodiv Development Area Development ersity/threatened/species/pubs/9338- Scheme. Queensland, Department of conservation-advice.pdf. In effect State Development, Infrastructure and under the EPBC Act from 01-Oct-2008. Planning.

Department of Sustainability, Environment, EDQ (2015). Environmental values and Water, Population and Communities sustainable resource use. PDA guideline (DSEWPaC) (2013). Conservation no. 14. Economic Development Advice for subtropical and temperate Queensland. coastal saltmarsh. Canberra: Department of Sustainability, Environment, Water, Neldner, V.J et al (2019). Methodology for Population and Communities. Available Survey and Mapping of Regional from: Ecosystems and Vegetation Communities http://www.environment.gov.au/biodiversi in Queensland, Version 4.0. Queensland ty/threatened/communities/pubs/118- Herbarium, Queensland Department of conservation-advice.pdf. Science, Information Technology, Innovation and the Arts, Brisbane. Department of the Environment, Water Heritage and the Arts (DEWHA) (2009). Significant impact guidelines for 36 migratory shorebird species – Migratory Species. EPBC Act Policy Statement 3.21. Commonwealth.

Department of the Environment and Energy (DoEE) (2018).Conservation advice (incorporating listing advice) for the Coastal Swamp Oak (Casuarina glauca) Forest of New South Wales and South East Queensland ecological community. Canberra: Department of the

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1.0 DRAWN CHECK STATUS SCALE CLIENT PROJECT DRAWING TITLE REVISION DATE ISSUE DETAILS DRAWN DESIGN ROADWORKS & DRAINAGE 1 17.12.20 ISSUED FOR INFORMATION RT CH PRELIMINARY WEINAM CREEK 2 13.01.21 RE-ISSUED FOR INFORMATION CH CH 1:250 5 0 5 10m A1 STAGE 2 LAYOUT PLAN DESIGN CHECK APPROVED 1:500 A3

PROJECT No. DRAWING No. REVISION REDLANDS INVESTMENT DISCLAIMER ALL DIMENSIONS TO BE CHECKED ON SITE BY CONTRACTOR PRIOR TO C calibregroup.com 20-000655 SK103 2 FOR & ON BEHALF OF CALIBRE PROFESSIONAL SERVICES PTY LTD CORPORATION CONSTRUCTION. USE WRITTEN DIMENSIONS ONLY, DO NOT SCALE. APPENDIX 2

Database Search Results EPBC Act Protected Matters Report

This report provides general guidance on matters of national environmental significance and other matters protected by the EPBC Act in the area you have selected.

Information on the coverage of this report and qualifications on data supporting this report are contained in the caveat at the end of the report.

Information is available about Environment Assessments and the EPBC Act including significance guidelines, forms and application process details.

Report created: 21/06/19 11:02:33

Summary Details Matters of NES Other Matters Protected by the EPBC Act Extra Information Caveat Acknowledgements

This map may contain data which are ©Commonwealth of Australia (Geoscience Australia), ©PSMA 2010

Coordinates Buffer: 2.0Km Summary

Matters of National Environmental Significance

This part of the report summarises the matters of national environmental significance that may occur in, or may relate to, the area you nominated. Further information is available in the detail part of the report, which can be accessed by scrolling or following the links below. If you are proposing to undertake an activity that may have a significant impact on one or more matters of national environmental significance then you should consider the Administrative Guidelines on Significance.

World Heritage Properties: None National Heritage Places: None Wetlands of International Importance: 25 Great Barrier Reef Marine Park: None Commonwealth Marine Area: None Listed Threatened Ecological Communities: 3 Listed Threatened Species: 65 Listed Migratory Species: 74

Other Matters Protected by the EPBC Act

This part of the report summarises other matters protected under the Act that may relate to the area you nominated. Approval may be required for a proposed activity that significantly affects the environment on Commonwealth land, when the action is outside the Commonwealth land, or the environment anywhere when the action is taken on Commonwealth land. Approval may also be required for the Commonwealth or Commonwealth agencies proposing to take an action that is likely to have a significant impact on the environment anywhere.

The EPBC Act protects the environment on Commonwealth land, the environment from the actions taken on Commonwealth land, and the environment from actions taken by Commonwealth agencies. As heritage values of a place are part of the 'environment', these aspects of the EPBC Act protect the Commonwealth Heritage values of a Commonwealth Heritage place. Information on the new heritage laws can be found at http://www.environment.gov.au/heritage

A permit may be required for activities in or on a Commonwealth area that may affect a member of a listed threatened species or ecological community, a member of a listed migratory species, whales and other cetaceans, or a member of a listed marine species.

Commonwealth Land: None Commonwealth Heritage Places: None Listed Marine Species: 107 Whales and Other Cetaceans: 13 Critical Habitats: None Commonwealth Reserves Terrestrial: None Australian Marine Parks: None

Extra Information

This part of the report provides information that may also be relevant to the area you have nominated.

State and Territory Reserves: None Regional Forest Agreements: None Invasive Species: 34 Nationally Important Wetlands: 1 Key Ecological Features (Marine) None Details

Matters of National Environmental Significance Wetlands of International Importance (Ramsar) [ Resource Information ] Name Proximity Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site Moreton bay Within Ramsar site

Listed Threatened Ecological Communities [ Resource Information ] For threatened ecological communities where the distribution is well known, maps are derived from recovery plans, State vegetation maps, remote sensing imagery and other sources. Where threatened ecological community distributions are less well known, existing vegetation maps and point location data are used to produce indicative distribution maps. Name Status Type of Presence Coastal Swamp Oak (Casuarina glauca) Forest of New Endangered Community may occur South Wales and South East Queensland ecological within area community Lowland Rainforest of Subtropical Australia Critically Endangered Community may occur within area Subtropical and Temperate Coastal Saltmarsh Vulnerable Community likely to occur within area Listed Threatened Species [ Resource Information ] Name Status Type of Presence Birds Anthochaera phrygia Regent Honeyeater [82338] Critically Endangered Foraging, feeding or related behaviour likely to occur within area Botaurus poiciloptilus Australasian Bittern [1001] Endangered Species or species habitat known to occur within area Name Status Type of Presence Calidris canutus Red Knot, Knot [855] Endangered Species or species habitat known to occur within area

Calidris ferruginea Curlew Sandpiper [856] Critically Endangered Species or species habitat likely to occur within area

Calidris tenuirostris Great Knot [862] Critically Endangered Species or species habitat known to occur within area

Charadrius leschenaultii Greater Sand Plover, Large Sand Plover [877] Vulnerable Species or species habitat known to occur within area

Charadrius mongolus Lesser Sand Plover, Mongolian Plover [879] Endangered Species or species habitat known to occur within area

Dasyornis brachypterus Eastern Bristlebird [533] Endangered Species or species habitat may occur within area

Diomedea antipodensis Antipodean Albatross [64458] Vulnerable Species or species habitat may occur within area

Diomedea antipodensis gibsoni Gibson's Albatross [82270] Vulnerable Species or species habitat may occur within area

Diomedea exulans Wandering Albatross [89223] Vulnerable Species or species habitat may occur within area

Erythrotriorchis radiatus Red Goshawk [942] Vulnerable Species or species habitat likely to occur within area

Fregetta grallaria grallaria White-bellied Storm-Petrel (Tasman Sea), White- Vulnerable Species or species habitat bellied Storm-Petrel (Australasian) [64438] likely to occur within area

Geophaps scripta scripta Squatter Pigeon (southern) [64440] Vulnerable Species or species habitat may occur within area

Lathamus discolor Swift Parrot [744] Critically Endangered Species or species habitat likely to occur within area

Limosa lapponica baueri Bar-tailed Godwit (baueri), Western Alaskan Bar-tailed Vulnerable Species or species habitat Godwit [86380] known to occur within area

Limosa lapponica menzbieri Northern Siberian Bar-tailed Godwit, Bar-tailed Godwit Critically Endangered Species or species habitat (menzbieri) [86432] may occur within area

Macronectes giganteus Southern Giant-Petrel, Southern Giant Petrel [1060] Endangered Species or species habitat may occur within area

Macronectes halli Northern Giant Petrel [1061] Vulnerable Species or species habitat may occur within area

Numenius madagascariensis Eastern Curlew, Far Eastern Curlew [847] Critically Endangered Species or species habitat known to occur within area Name Status Type of Presence Pachyptila turtur subantarctica Fairy Prion (southern) [64445] Vulnerable Species or species habitat likely to occur within area

Poephila cincta cincta Southern Black-throated Finch [64447] Endangered Species or species habitat may occur within area

Pterodroma neglecta neglecta Kermadec Petrel (western) [64450] Vulnerable Foraging, feeding or related behaviour may occur within area Rostratula australis Australian Painted-snipe, Australian Painted Snipe Endangered Species or species habitat [77037] likely to occur within area

Thalassarche cauta cauta Shy Albatross, Tasmanian Shy Albatross [82345] Vulnerable Species or species habitat may occur within area

Thalassarche cauta steadi White-capped Albatross [82344] Vulnerable Foraging, feeding or related behaviour likely to occur within area Thalassarche eremita Chatham Albatross [64457] Endangered Species or species habitat may occur within area

Thalassarche impavida Campbell Albatross, Campbell Black-browed Albatross Vulnerable Species or species habitat [64459] may occur within area

Thalassarche melanophris Black-browed Albatross [66472] Vulnerable Species or species habitat may occur within area

Thalassarche salvini Salvin's Albatross [64463] Vulnerable Species or species habitat may occur within area

Turnix melanogaster Black-breasted Button-quail [923] Vulnerable Species or species habitat likely to occur within area

Fish Epinephelus daemelii Black Rockcod, Black Cod, Saddled Rockcod [68449] Vulnerable Species or species habitat may occur within area

Insects Argynnis hyperbius inconstans Australian Fritillary [88056] Critically Endangered Species or species habitat may occur within area

Mammals Balaenoptera musculus Blue Whale [36] Endangered Species or species habitat may occur within area

Chalinolobus dwyeri Large-eared Pied Bat, Large Pied Bat [183] Vulnerable Species or species habitat may occur within area

Dasyurus maculatus maculatus (SE mainland population) Spot-tailed Quoll, Spotted-tail Quoll, Tiger Quoll Endangered Species or species habitat (southeastern mainland population) [75184] likely to occur within area

Eubalaena australis Southern Right Whale [40] Endangered Species or species habitat likely to occur within area

Megaptera novaeangliae Humpback Whale [38] Vulnerable Species or species Name Status Type of Presence habitat known to occur within area Petauroides volans Greater Glider [254] Vulnerable Species or species habitat may occur within area

Phascolarctos cinereus (combined populations of Qld, NSW and the ACT) Koala (combined populations of Queensland, New Vulnerable Species or species habitat South Wales and the Australian Capital Territory) known to occur within area [85104] Potorous tridactylus tridactylus Long-nosed Potoroo (SE mainland) [66645] Vulnerable Species or species habitat may occur within area

Pteropus poliocephalus Grey-headed Flying-fox [186] Vulnerable Roosting known to occur within area Xeromys myoides Water Mouse, False Water Rat, Yirrkoo [66] Vulnerable Species or species habitat likely to occur within area

Plants Arthraxon hispidus Hairy-joint Grass [9338] Vulnerable Species or species habitat may occur within area

Baloghia marmorata Marbled Balogia, Jointed Baloghia [8463] Vulnerable Species or species habitat may occur within area

Corchorus cunninghamii Native Jute [14659] Endangered Species or species habitat likely to occur within area

Cryptocarya foetida Stinking Cryptocarya, Stinking Laurel [11976] Vulnerable Species or species habitat may occur within area

Cryptostylis hunteriana Leafless Tongue-orchid [19533] Vulnerable Species or species habitat may occur within area

Endiandra floydii Floyd's Walnut [52955] Endangered Species or species habitat likely to occur within area

Macadamia integrifolia Macadamia Nut, Queensland Nut Tree, Smooth- Vulnerable Species or species habitat shelled Macadamia, Bush Nut, Nut Oak [7326] may occur within area

Macadamia tetraphylla Rough-shelled Bush Nut, Macadamia Nut, Rough- Vulnerable Species or species habitat shelled Macadamia, Rough-leaved Queensland Nut may occur within area [6581] Phaius australis Lesser Swamp-orchid [5872] Endangered Species or species habitat likely to occur within area

Samadera bidwillii Quassia [29708] Vulnerable Species or species habitat likely to occur within area

Thesium australe Austral Toadflax, Toadflax [15202] Vulnerable Species or species habitat may occur within area

Reptiles Caretta caretta Loggerhead Turtle [1763] Endangered Breeding known to occur within area Chelonia mydas Green Turtle [1765] Vulnerable Foraging, feeding or related behaviour known Name Status Type of Presence to occur within area Delma torquata Adorned Delma, Collared Delma [1656] Vulnerable Species or species habitat may occur within area

Dermochelys coriacea Leatherback Turtle, Leathery Turtle, Luth [1768] Endangered Species or species habitat known to occur within area

Eretmochelys imbricata Hawksbill Turtle [1766] Vulnerable Species or species habitat known to occur within area

Lepidochelys olivacea Olive Ridley Turtle, Pacific Ridley Turtle [1767] Endangered Species or species habitat known to occur within area

Natator depressus Flatback Turtle [59257] Vulnerable Foraging, feeding or related behaviour known to occur within area Sharks Carcharias taurus (east coast population) Grey Nurse Shark (east coast population) [68751] Critically Endangered Species or species habitat likely to occur within area

Carcharodon carcharias White Shark, Great White Shark [64470] Vulnerable Species or species habitat known to occur within area

Pristis zijsron Green Sawfish, Dindagubba, Narrowsnout Sawfish Vulnerable Breeding may occur within [68442] area Rhincodon typus Whale Shark [66680] Vulnerable Species or species habitat may occur within area

Listed Migratory Species [ Resource Information ] * Species is listed under a different scientific name on the EPBC Act - Threatened Species list. Name Threatened Type of Presence Migratory Marine Birds Anous stolidus Common Noddy [825] Species or species habitat likely to occur within area

Apus pacificus Fork-tailed Swift [678] Species or species habitat likely to occur within area

Ardenna carneipes Flesh-footed Shearwater, Fleshy-footed Shearwater Species or species habitat [82404] likely to occur within area

Calonectris leucomelas Streaked Shearwater [1077] Species or species habitat known to occur within area

Diomedea antipodensis Antipodean Albatross [64458] Vulnerable Species or species habitat may occur within area

Diomedea exulans Wandering Albatross [89223] Vulnerable Species or species habitat may occur within area

Fregata ariel Lesser Frigatebird, Least Frigatebird [1012] Species or species habitat likely to occur within area

Fregata minor Great Frigatebird, Greater Frigatebird [1013] Species or species Name Threatened Type of Presence habitat likely to occur within area Macronectes giganteus Southern Giant-Petrel, Southern Giant Petrel [1060] Endangered Species or species habitat may occur within area

Macronectes halli Northern Giant Petrel [1061] Vulnerable Species or species habitat may occur within area

Sternula albifrons Little Tern [82849] Species or species habitat may occur within area

Thalassarche cauta Tasmanian Shy Albatross [89224] Vulnerable* Species or species habitat may occur within area

Thalassarche eremita Chatham Albatross [64457] Endangered Species or species habitat may occur within area

Thalassarche impavida Campbell Albatross, Campbell Black-browed Albatross Vulnerable Species or species habitat [64459] may occur within area

Thalassarche melanophris Black-browed Albatross [66472] Vulnerable Species or species habitat may occur within area

Thalassarche salvini Salvin's Albatross [64463] Vulnerable Species or species habitat may occur within area

Thalassarche steadi White-capped Albatross [64462] Vulnerable* Foraging, feeding or related behaviour likely to occur within area Migratory Marine Species Balaena glacialis australis Southern Right Whale [75529] Endangered* Species or species habitat likely to occur within area

Balaenoptera edeni Bryde's Whale [35] Species or species habitat may occur within area

Balaenoptera musculus Blue Whale [36] Endangered Species or species habitat may occur within area

Carcharodon carcharias White Shark, Great White Shark [64470] Vulnerable Species or species habitat known to occur within area

Caretta caretta Loggerhead Turtle [1763] Endangered Breeding known to occur within area Chelonia mydas Green Turtle [1765] Vulnerable Foraging, feeding or related behaviour known to occur within area Dermochelys coriacea Leatherback Turtle, Leathery Turtle, Luth [1768] Endangered Species or species habitat known to occur within area

Dugong dugon Dugong [28] Species or species habitat known to occur within area

Eretmochelys imbricata Hawksbill Turtle [1766] Vulnerable Species or species habitat known to occur Name Threatened Type of Presence within area Lamna nasus Porbeagle, Mackerel Shark [83288] Species or species habitat may occur within area

Lepidochelys olivacea Olive Ridley Turtle, Pacific Ridley Turtle [1767] Endangered Species or species habitat known to occur within area

Manta alfredi Reef Manta Ray, Coastal Manta Ray, Inshore Manta Species or species habitat Ray, Prince Alfred's Ray, Resident Manta Ray [84994] may occur within area

Manta birostris Giant Manta Ray, Chevron Manta Ray, Pacific Manta Species or species habitat Ray, Pelagic Manta Ray, Oceanic Manta Ray [84995] may occur within area

Megaptera novaeangliae Humpback Whale [38] Vulnerable Species or species habitat known to occur within area

Natator depressus Flatback Turtle [59257] Vulnerable Foraging, feeding or related behaviour known to occur within area Orcaella heinsohni Australian Snubfin Dolphin [81322] Species or species habitat likely to occur within area

Orcinus orca Killer Whale, Orca [46] Species or species habitat may occur within area

Pristis zijsron Green Sawfish, Dindagubba, Narrowsnout Sawfish Vulnerable Breeding may occur within [68442] area Rhincodon typus Whale Shark [66680] Vulnerable Species or species habitat may occur within area

Sousa chinensis Indo-Pacific Humpback Dolphin [50] Breeding known to occur within area Migratory Terrestrial Species Cuculus optatus Oriental Cuckoo, Horsfield's Cuckoo [86651] Species or species habitat known to occur within area

Hirundapus caudacutus White-throated Needletail [682] Species or species habitat known to occur within area

Monarcha melanopsis Black-faced Monarch [609] Species or species habitat known to occur within area

Monarcha trivirgatus Spectacled Monarch [610] Species or species habitat likely to occur within area

Myiagra cyanoleuca Satin Flycatcher [612] Species or species habitat known to occur within area

Rhipidura rufifrons Rufous Fantail [592] Species or species habitat likely to occur within area

Migratory Wetlands Species Actitis hypoleucos Common Sandpiper [59309] Species or species habitat likely to occur within area Name Threatened Type of Presence Arenaria interpres Ruddy Turnstone [872] Species or species habitat known to occur within area

Calidris acuminata Sharp-tailed Sandpiper [874] Species or species habitat known to occur within area

Calidris alba Sanderling [875] Species or species habitat known to occur within area

Calidris canutus Red Knot, Knot [855] Endangered Species or species habitat known to occur within area

Calidris ferruginea Curlew Sandpiper [856] Critically Endangered Species or species habitat likely to occur within area

Calidris melanotos Pectoral Sandpiper [858] Species or species habitat may occur within area

Calidris ruficollis Red-necked Stint [860] Species or species habitat known to occur within area

Calidris tenuirostris Great Knot [862] Critically Endangered Species or species habitat known to occur within area

Charadrius bicinctus Double-banded Plover [895] Species or species habitat known to occur within area

Charadrius leschenaultii Greater Sand Plover, Large Sand Plover [877] Vulnerable Species or species habitat known to occur within area

Charadrius mongolus Lesser Sand Plover, Mongolian Plover [879] Endangered Species or species habitat known to occur within area

Charadrius veredus Oriental Plover, Oriental Dotterel [882] Species or species habitat known to occur within area

Gallinago hardwickii Latham's Snipe, Japanese Snipe [863] Species or species habitat known to occur within area

Limicola falcinellus Broad-billed Sandpiper [842] Species or species habitat known to occur within area

Limnodromus semipalmatus Asian Dowitcher [843] Species or species habitat known to occur within area

Limosa lapponica Bar-tailed Godwit [844] Species or species habitat known to occur within area

Limosa limosa Black-tailed Godwit [845] Species or species habitat known to occur within area

Numenius madagascariensis Eastern Curlew, Far Eastern Curlew [847] Critically Endangered Species or species habitat known to occur within area Name Threatened Type of Presence Numenius minutus Little Curlew, Little Whimbrel [848] Species or species habitat known to occur within area

Numenius phaeopus Whimbrel [849] Species or species habitat known to occur within area

Pandion haliaetus Osprey [952] Breeding known to occur within area Philomachus pugnax Ruff (Reeve) [850] Species or species habitat known to occur within area

Pluvialis fulva Pacific Golden Plover [25545] Species or species habitat known to occur within area

Pluvialis squatarola Grey Plover [865] Species or species habitat known to occur within area

Tringa brevipes Grey-tailed Tattler [851] Species or species habitat known to occur within area

Tringa glareola Wood Sandpiper [829] Species or species habitat known to occur within area

Tringa incana Wandering Tattler [831] Species or species habitat known to occur within area

Tringa nebularia Common Greenshank, Greenshank [832] Species or species habitat known to occur within area

Tringa stagnatilis Marsh Sandpiper, Little Greenshank [833] Species or species habitat known to occur within area

Xenus cinereus Terek Sandpiper [59300] Species or species habitat known to occur within area

Other Matters Protected by the EPBC Act Listed Marine Species [ Resource Information ] * Species is listed under a different scientific name on the EPBC Act - Threatened Species list. Name Threatened Type of Presence Birds Actitis hypoleucos Common Sandpiper [59309] Species or species habitat likely to occur within area

Anous stolidus Common Noddy [825] Species or species habitat likely to occur within area

Anseranas semipalmata Magpie Goose [978] Species or species habitat may occur within area

Apus pacificus Fork-tailed Swift [678] Species or species Name Threatened Type of Presence habitat likely to occur within area Ardea alba Great Egret, White Egret [59541] Breeding known to occur within area Ardea ibis Cattle Egret [59542] Species or species habitat may occur within area

Arenaria interpres Ruddy Turnstone [872] Species or species habitat known to occur within area

Calidris acuminata Sharp-tailed Sandpiper [874] Species or species habitat known to occur within area

Calidris alba Sanderling [875] Species or species habitat known to occur within area

Calidris canutus Red Knot, Knot [855] Endangered Species or species habitat known to occur within area

Calidris ferruginea Curlew Sandpiper [856] Critically Endangered Species or species habitat likely to occur within area

Calidris melanotos Pectoral Sandpiper [858] Species or species habitat may occur within area

Calidris ruficollis Red-necked Stint [860] Species or species habitat known to occur within area

Calidris tenuirostris Great Knot [862] Critically Endangered Species or species habitat known to occur within area

Calonectris leucomelas Streaked Shearwater [1077] Species or species habitat known to occur within area

Charadrius bicinctus Double-banded Plover [895] Species or species habitat known to occur within area

Charadrius leschenaultii Greater Sand Plover, Large Sand Plover [877] Vulnerable Species or species habitat known to occur within area

Charadrius mongolus Lesser Sand Plover, Mongolian Plover [879] Endangered Species or species habitat known to occur within area

Charadrius ruficapillus Red-capped Plover [881] Species or species habitat known to occur within area

Charadrius veredus Oriental Plover, Oriental Dotterel [882] Species or species habitat known to occur within area

Diomedea antipodensis Antipodean Albatross [64458] Vulnerable Species or species habitat may occur within area

Diomedea exulans Wandering Albatross [89223] Vulnerable Species or species habitat may occur within area Name Threatened Type of Presence Diomedea gibsoni Gibson's Albatross [64466] Vulnerable* Species or species habitat may occur within area

Fregata ariel Lesser Frigatebird, Least Frigatebird [1012] Species or species habitat likely to occur within area

Fregata minor Great Frigatebird, Greater Frigatebird [1013] Species or species habitat likely to occur within area

Gallinago hardwickii Latham's Snipe, Japanese Snipe [863] Species or species habitat known to occur within area

Haliaeetus leucogaster White-bellied Sea-Eagle [943] Species or species habitat known to occur within area

Heteroscelus brevipes Grey-tailed Tattler [59311] Species or species habitat known to occur within area

Heteroscelus incanus Wandering Tattler [59547] Species or species habitat known to occur within area

Himantopus himantopus Pied Stilt, Black-winged Stilt [870] Species or species habitat known to occur within area

Hirundapus caudacutus White-throated Needletail [682] Species or species habitat known to occur within area

Lathamus discolor Swift Parrot [744] Critically Endangered Species or species habitat likely to occur within area

Limicola falcinellus Broad-billed Sandpiper [842] Species or species habitat known to occur within area

Limnodromus semipalmatus Asian Dowitcher [843] Species or species habitat known to occur within area

Limosa lapponica Bar-tailed Godwit [844] Species or species habitat known to occur within area

Limosa limosa Black-tailed Godwit [845] Species or species habitat known to occur within area

Macronectes giganteus Southern Giant-Petrel, Southern Giant Petrel [1060] Endangered Species or species habitat may occur within area

Macronectes halli Northern Giant Petrel [1061] Vulnerable Species or species habitat may occur within area

Merops ornatus Rainbow Bee-eater [670] Species or species habitat may occur within area

Monarcha melanopsis Black-faced Monarch [609] Species or species habitat known to occur within area Name Threatened Type of Presence Monarcha trivirgatus Spectacled Monarch [610] Species or species habitat likely to occur within area

Myiagra cyanoleuca Satin Flycatcher [612] Species or species habitat known to occur within area

Numenius madagascariensis Eastern Curlew, Far Eastern Curlew [847] Critically Endangered Species or species habitat known to occur within area

Numenius minutus Little Curlew, Little Whimbrel [848] Species or species habitat known to occur within area

Numenius phaeopus Whimbrel [849] Species or species habitat known to occur within area

Pachyptila turtur Fairy Prion [1066] Species or species habitat likely to occur within area

Pandion haliaetus Osprey [952] Breeding known to occur within area Philomachus pugnax Ruff (Reeve) [850] Species or species habitat known to occur within area

Pluvialis fulva Pacific Golden Plover [25545] Species or species habitat known to occur within area

Pluvialis squatarola Grey Plover [865] Species or species habitat known to occur within area

Puffinus carneipes Flesh-footed Shearwater, Fleshy-footed Shearwater Species or species habitat [1043] likely to occur within area

Recurvirostra novaehollandiae Red-necked Avocet [871] Species or species habitat known to occur within area

Rhipidura rufifrons Rufous Fantail [592] Species or species habitat likely to occur within area

Rostratula benghalensis (sensu lato) Painted Snipe [889] Endangered* Species or species habitat likely to occur within area

Sterna albifrons Little Tern [813] Species or species habitat may occur within area

Thalassarche cauta Tasmanian Shy Albatross [89224] Vulnerable* Species or species habitat may occur within area

Thalassarche eremita Chatham Albatross [64457] Endangered Species or species habitat may occur within area

Thalassarche impavida Campbell Albatross, Campbell Black-browed Albatross Vulnerable Species or species habitat [64459] may occur within area

Thalassarche melanophris Black-browed Albatross [66472] Vulnerable Species or species Name Threatened Type of Presence habitat may occur within area Thalassarche salvini Salvin's Albatross [64463] Vulnerable Species or species habitat may occur within area

Thalassarche steadi White-capped Albatross [64462] Vulnerable* Foraging, feeding or related behaviour likely to occur within area Tringa glareola Wood Sandpiper [829] Species or species habitat known to occur within area

Tringa nebularia Common Greenshank, Greenshank [832] Species or species habitat known to occur within area

Tringa stagnatilis Marsh Sandpiper, Little Greenshank [833] Species or species habitat known to occur within area

Xenus cinereus Terek Sandpiper [59300] Species or species habitat known to occur within area

Fish Acentronura tentaculata Shortpouch Pygmy Pipehorse [66187] Species or species habitat may occur within area

Campichthys tryoni Tryon's Pipefish [66193] Species or species habitat may occur within area

Corythoichthys amplexus Fijian Banded Pipefish, Brown-banded Pipefish Species or species habitat [66199] may occur within area

Corythoichthys ocellatus Orange-spotted Pipefish, Ocellated Pipefish [66203] Species or species habitat may occur within area

Festucalex cinctus Girdled Pipefish [66214] Species or species habitat may occur within area

Filicampus tigris Tiger Pipefish [66217] Species or species habitat may occur within area

Halicampus grayi Mud Pipefish, Gray's Pipefish [66221] Species or species habitat may occur within area

Hippichthys cyanospilos Blue-speckled Pipefish, Blue-spotted Pipefish [66228] Species or species habitat may occur within area

Hippichthys heptagonus Madura Pipefish, Reticulated Freshwater Pipefish Species or species habitat [66229] may occur within area

Hippichthys penicillus Beady Pipefish, Steep-nosed Pipefish [66231] Species or species habitat may occur within area

Hippocampus kelloggi Kellogg's Seahorse, Great Seahorse [66723] Species or species habitat may occur within area

Hippocampus kuda Spotted Seahorse, Yellow Seahorse [66237] Species or species Name Threatened Type of Presence habitat may occur within area Hippocampus planifrons Flat-face Seahorse [66238] Species or species habitat may occur within area

Hippocampus trimaculatus Three-spot Seahorse, Low-crowned Seahorse, Flat- Species or species habitat faced Seahorse [66720] may occur within area

Hippocampus whitei White's Seahorse, Crowned Seahorse, Sydney Species or species habitat Seahorse [66240] likely to occur within area

Lissocampus runa Javelin Pipefish [66251] Species or species habitat may occur within area

Maroubra perserrata Sawtooth Pipefish [66252] Species or species habitat may occur within area

Micrognathus andersonii Anderson's Pipefish, Shortnose Pipefish [66253] Species or species habitat may occur within area

Micrognathus brevirostris thorntail Pipefish, Thorn-tailed Pipefish [66254] Species or species habitat may occur within area

Microphis manadensis Manado Pipefish, Manado River Pipefish [66258] Species or species habitat may occur within area

Solegnathus dunckeri Duncker's Pipehorse [66271] Species or species habitat may occur within area

Solegnathus hardwickii Pallid Pipehorse, Hardwick's Pipehorse [66272] Species or species habitat may occur within area

Solegnathus spinosissimus Spiny Pipehorse, Australian Spiny Pipehorse [66275] Species or species habitat may occur within area

Solenostomus cyanopterus Robust Ghostpipefish, Blue-finned Ghost Pipefish, Species or species habitat [66183] may occur within area

Solenostomus paradoxus Ornate Ghostpipefish, Harlequin Ghost Pipefish, Species or species habitat Ornate Ghost Pipefish [66184] may occur within area

Stigmatopora nigra Widebody Pipefish, Wide-bodied Pipefish, Black Species or species habitat Pipefish [66277] may occur within area

Syngnathoides biaculeatus Double-end Pipehorse, Double-ended Pipehorse, Species or species habitat Alligator Pipefish [66279] may occur within area

Trachyrhamphus bicoarctatus Bentstick Pipefish, Bend Stick Pipefish, Short-tailed Species or species habitat Pipefish [66280] may occur within area

Urocampus carinirostris Hairy Pipefish [66282] Species or species habitat may occur within area

Vanacampus margaritifer Mother-of-pearl Pipefish [66283] Species or species habitat may occur within Name Threatened Type of Presence area Mammals Dugong dugon Dugong [28] Species or species habitat known to occur within area

Reptiles Aipysurus laevis Olive Seasnake [1120] Species or species habitat may occur within area

Astrotia stokesii Stokes' Seasnake [1122] Species or species habitat may occur within area

Caretta caretta Loggerhead Turtle [1763] Endangered Breeding known to occur within area Chelonia mydas Green Turtle [1765] Vulnerable Foraging, feeding or related behaviour known to occur within area Dermochelys coriacea Leatherback Turtle, Leathery Turtle, Luth [1768] Endangered Species or species habitat known to occur within area

Eretmochelys imbricata Hawksbill Turtle [1766] Vulnerable Species or species habitat known to occur within area

Hydrophis elegans Elegant Seasnake [1104] Species or species habitat may occur within area

Laticauda laticaudata a sea krait [1093] Species or species habitat may occur within area

Lepidochelys olivacea Olive Ridley Turtle, Pacific Ridley Turtle [1767] Endangered Species or species habitat known to occur within area

Natator depressus Flatback Turtle [59257] Vulnerable Foraging, feeding or related behaviour known to occur within area Pelamis platurus Yellow-bellied Seasnake [1091] Species or species habitat may occur within area

Whales and other Cetaceans [ Resource Information ] Name Status Type of Presence Mammals Balaenoptera acutorostrata Minke Whale [33] Species or species habitat may occur within area

Balaenoptera edeni Bryde's Whale [35] Species or species habitat may occur within area

Balaenoptera musculus Blue Whale [36] Endangered Species or species habitat may occur within area

Delphinus delphis Common Dophin, Short-beaked Common Dolphin [60] Species or species habitat may occur within area

Eubalaena australis Southern Right Whale [40] Endangered Species or species Name Status Type of Presence habitat likely to occur within area Grampus griseus Risso's Dolphin, Grampus [64] Species or species habitat may occur within area

Megaptera novaeangliae Humpback Whale [38] Vulnerable Species or species habitat known to occur within area

Orcaella brevirostris Irrawaddy Dolphin [45] Species or species habitat likely to occur within area

Orcinus orca Killer Whale, Orca [46] Species or species habitat may occur within area

Sousa chinensis Indo-Pacific Humpback Dolphin [50] Breeding known to occur within area Stenella attenuata Spotted Dolphin, Pantropical Spotted Dolphin [51] Species or species habitat may occur within area

Tursiops aduncus Indian Ocean Bottlenose Dolphin, Spotted Bottlenose Species or species habitat Dolphin [68418] likely to occur within area

Tursiops truncatus s. str. Bottlenose Dolphin [68417] Species or species habitat may occur within area

Extra Information Invasive Species [ Resource Information ] Weeds reported here are the 20 species of national significance (WoNS), along with other introduced plants that are considered by the States and Territories to pose a particularly significant threat to biodiversity. The following feral animals are reported: Goat, Red Fox, Cat, Rabbit, Pig, Water Buffalo and Cane Toad. Maps from Landscape Health Project, National Land and Water Resouces Audit, 2001.

Name Status Type of Presence Birds Acridotheres tristis Common Myna, Indian Myna [387] Species or species habitat likely to occur within area

Anas platyrhynchos Mallard [974] Species or species habitat likely to occur within area

Carduelis carduelis European Goldfinch [403] Species or species habitat likely to occur within area

Columba livia Rock Pigeon, Rock Dove, Domestic Pigeon [803] Species or species habitat likely to occur within area

Lonchura punctulata Nutmeg Mannikin [399] Species or species habitat likely to occur within area

Passer domesticus House Sparrow [405] Species or species habitat likely to occur within area Name Status Type of Presence Streptopelia chinensis Spotted Turtle-Dove [780] Species or species habitat likely to occur within area

Sturnus vulgaris Common Starling [389] Species or species habitat likely to occur within area

Frogs Rhinella marina Cane Toad [83218] Species or species habitat known to occur within area

Mammals Bos taurus Domestic Cattle [16] Species or species habitat likely to occur within area

Canis lupus familiaris Domestic Dog [82654] Species or species habitat likely to occur within area

Felis catus Cat, House Cat, Domestic Cat [19] Species or species habitat likely to occur within area

Lepus capensis Brown Hare [127] Species or species habitat likely to occur within area

Mus musculus House Mouse [120] Species or species habitat likely to occur within area

Oryctolagus cuniculus Rabbit, European Rabbit [128] Species or species habitat likely to occur within area

Rattus norvegicus Brown Rat, Norway Rat [83] Species or species habitat likely to occur within area

Rattus rattus Black Rat, Ship Rat [84] Species or species habitat likely to occur within area

Sus scrofa Pig [6] Species or species habitat likely to occur within area

Vulpes vulpes Red Fox, Fox [18] Species or species habitat likely to occur within area

Plants Alternanthera philoxeroides Alligator Weed [11620] Species or species habitat likely to occur within area

Asparagus aethiopicus Asparagus Fern, Ground Asparagus, Basket Fern, Species or species habitat Sprengi's Fern, Bushy Asparagus, Emerald Asparagus likely to occur within area [62425] Cabomba caroliniana Cabomba, Fanwort, Carolina Watershield, Fish Grass, Species or species habitat Washington Grass, Watershield, Carolina Fanwort, likely to occur within area Common Cabomba [5171] Chrysanthemoides monilifera Bitou Bush, Boneseed [18983] Species or species habitat may occur within area

Chrysanthemoides monilifera subsp. rotundata Bitou Bush [16332] Species or species Name Status Type of Presence habitat likely to occur within area Cryptostegia grandiflora Rubber Vine, Rubbervine, India Rubber Vine, India Species or species habitat Rubbervine, Palay Rubbervine, Purple Allamanda likely to occur within area [18913] Eichhornia crassipes Water Hyacinth, Water Orchid, Nile Lily [13466] Species or species habitat likely to occur within area

Hymenachne amplexicaulis Hymenachne, Olive Hymenachne, Water Stargrass, Species or species habitat West Indian Grass, West Indian Marsh Grass [31754] likely to occur within area

Lantana camara Lantana, Common Lantana, Kamara Lantana, Large- Species or species habitat leaf Lantana, Pink Flowered Lantana, Red Flowered likely to occur within area Lantana, Red-Flowered Sage, White Sage, Wild Sage [10892] Parthenium hysterophorus Parthenium Weed, Bitter Weed, Carrot Grass, False Species or species habitat Ragweed [19566] likely to occur within area

Salix spp. except S.babylonica, S.x calodendron & S.x reichardtii Willows except Weeping Willow, Pussy Willow and Species or species habitat Sterile Pussy Willow [68497] likely to occur within area

Salvinia molesta Salvinia, Giant Salvinia, Aquarium Watermoss, Kariba Species or species habitat Weed [13665] likely to occur within area

Senecio madagascariensis Fireweed, Madagascar Ragwort, Madagascar Species or species habitat Groundsel [2624] likely to occur within area

Reptiles Hemidactylus frenatus Asian House Gecko [1708] Species or species habitat likely to occur within area

Ramphotyphlops braminus Flowerpot Blind Snake, Brahminy Blind Snake, Cacing Species or species habitat Besi [1258] likely to occur within area

Nationally Important Wetlands [ Resource Information ] Name State Moreton Bay QLD Caveat The information presented in this report has been provided by a range of data sources as acknowledged at the end of the report.

This report is designed to assist in identifying the locations of places which may be relevant in determining obligations under the Environment Protection and Biodiversity Conservation Act 1999. It holds mapped locations of World and National Heritage properties, Wetlands of International and National Importance, Commonwealth and State/Territory reserves, listed threatened, migratory and marine species and listed threatened ecological communities. Mapping of Commonwealth land is not complete at this stage. Maps have been collated from a range of sources at various resolutions.

Not all species listed under the EPBC Act have been mapped (see below) and therefore a report is a general guide only. Where available data supports mapping, the type of presence that can be determined from the data is indicated in general terms. People using this information in making a referral may need to consider the qualifications below and may need to seek and consider other information sources.

For threatened ecological communities where the distribution is well known, maps are derived from recovery plans, State vegetation maps, remote sensing imagery and other sources. Where threatened ecological community distributions are less well known, existing vegetation maps and point location data are used to produce indicative distribution maps.

Threatened, migratory and marine species distributions have been derived through a variety of methods. Where distributions are well known and if time permits, maps are derived using either thematic spatial data (i.e. vegetation, soils, geology, elevation, aspect, terrain, etc) together with point locations and described habitat; or environmental modelling (MAXENT or BIOCLIM habitat modelling) using point locations and environmental data layers.

Where very little information is available for species or large number of maps are required in a short time-frame, maps are derived either from 0.04 or 0.02 decimal degree cells; by an automated process using polygon capture techniques (static two kilometre grid cells, alpha-hull and convex hull); or captured manually or by using topographic features (national park boundaries, islands, etc). In the early stages of the distribution mapping process (1999-early 2000s) distributions were defined by degree blocks, 100K or 250K map sheets to rapidly create distribution maps. More reliable distribution mapping methods are used to update these distributions as time permits.

Only selected species covered by the following provisions of the EPBC Act have been mapped: - migratory and - marine The following species and ecological communities have not been mapped and do not appear in reports produced from this database:

- threatened species listed as extinct or considered as vagrants - some species and ecological communities that have only recently been listed - some terrestrial species that overfly the Commonwealth marine area - migratory species that are very widespread, vagrant, or only occur in small numbers The following groups have been mapped, but may not cover the complete distribution of the species: - non-threatened seabirds which have only been mapped for recorded breeding sites - seals which have only been mapped for breeding sites near the Australian continent Such breeding sites may be important for the protection of the Commonwealth Marine environment.

Coordinates

-27.62067 153.3073 Acknowledgements This database has been compiled from a range of data sources. The department acknowledges the following custodians who have contributed valuable data and advice: -Office of Environment and Heritage, New South Wales -Department of Environment and Primary Industries, Victoria -Department of Primary Industries, Parks, Water and Environment, Tasmania -Department of Environment, Water and Natural Resources, South Australia -Department of Land and Resource Management, Northern Territory -Department of Environmental and Heritage Protection, Queensland -Department of Parks and Wildlife, Western Australia -Environment and Planning Directorate, ACT -Birdlife Australia -Australian Bird and Bat Banding Scheme -Australian National Wildlife Collection -Natural history museums of Australia -Museum Victoria -Australian Museum -South Australian Museum -Queensland Museum -Online Zoological Collections of Australian Museums -Queensland Herbarium -National Herbarium of NSW -Royal Botanic Gardens and National Herbarium of Victoria -Tasmanian Herbarium -State Herbarium of South Australia -Northern Territory Herbarium -Western Australian Herbarium -Australian National Herbarium, Canberra -University of New England -Ocean Biogeographic Information System -Australian Government, Department of Defence Forestry Corporation, NSW -Geoscience Australia -CSIRO -Australian Tropical Herbarium, Cairns -eBird Australia -Australian Government – Australian Antarctic Data Centre -Museum and Art Gallery of the Northern Territory -Australian Government National Environmental Science Program -Australian Institute of Marine Science -Reef Life Survey Australia -American Museum of Natural History -Queen Victoria Museum and Art Gallery, Inveresk, Tasmania -Tasmanian Museum and Art Gallery, Hobart, Tasmania -Other groups and individuals

The Department is extremely grateful to the many organisations and individuals who provided expert advice and information on numerous draft distributions.

Please feel free to provide feedback via the Contact Us page.

© Commonwealth of Australia Department of the Environment GPO Box 787 Canberra ACT 2601 Australia +61 2 6274 1111 Wildlife Online Extract

Search Criteria: Species List for a Specified Point Species: All Type: All Status: Rare and threatened species Records: Confirmed Date: Since 1980 Latitude: -27.6202 Longitude: 153.3079 Distance: 2 Email: [email protected] Date submitted: Tuesday 18 Jun 2019 10:54:30 Date extracted: Tuesday 18 Jun 2019 11:00:02 The number of records retrieved = 3

Disclaimer

As the DSITIA is still in a process of collating and vetting data, it is possible the information given is not complete. The information provided should only be used for the project for which it was requested and it should be appropriately acknowledged as being derived from Wildlife Online when it is used. The State of Queensland does not invite reliance upon, nor accept responsibility for this information. Persons should satisfy themselves through independent means as to the accuracy and completeness of this information. No statements, representations or warranties are made about the accuracy or completeness of this information. The State of Queensland disclaims all responsibility for this information and all liability (including without limitation, liability in negligence) for all expenses, losses, damages and costs you may incur as a result of the information being inaccurate or incomplete in any way for any reason.

Feedback about Wildlife Online should be emailed to [email protected] Kingdom Class Family Scientific Name Common Name I Q A Records animals birds Scolopacidae Numenius madagascariensis eastern curlew E CE 3 animals mammals Dugongidae Dugong dugon dugong V 1 animals mammals Phascolarctidae Phascolarctos cinereus koala V V 262

CODES I - Y indicates that the taxon is introduced to Queensland and has naturalised. Q - Indicates the Queensland conservation status of each taxon under the Nature Conservation Act 1992. The codes are Extinct in the Wild (PE), Endangered (E), Vulnerable (V), Near Threatened (NT), Least Concern (C) or Not Protected ( ). A - Indicates the Australian conservation status of each taxon under the Environment Protection and Biodiversity Conservation Act 1999. The values of EPBC are Conservation Dependent (CD), Critically Endangered (CE), Endangered (E), Extinct (EX), Extinct in the Wild (XW) and Vulnerable (V). Records – The first number indicates the total number of records of the taxon for the record option selected (i.e. All, Confirmed or Specimens). This number is output as 99999 if it equals or exceeds this value. The second number located after the / indicates the number of specimen records for the taxon. This number is output as 999 if it equals or exceeds this value.

Page 1 of 1 Queensland Government Wildlife Online - Extract Date 18/06/2019 at 11:00:02 APPENDIX 3

Matters of State Environmental Significance Mapping 21/06/2019 15:34:03 Lot: 1 Plan: RP90590

Page 1 21/06/2019 15:34:03 Lot: 1 Plan: RP90590

Page 2 21/06/2019 15:34:03 Lot: 1 Plan: RP90590

Vegetation Management Act 1999 - Extract from the essential habitat database

Essential habitat is required for assessment under the: • State Development Assessment Provisions - State Code 16: Native vegetation clearing which sets out the matters of interest to the state for development assessment under the Planning Act 2016; and • Accepted development vegetation clearing codes made under the Vegetation Management Act 1999

Essential habitat for one or more of the following species is found on and within 1.1 km of the identified subject lot/s on the accompanying essential habitat map. This report identifies essential habitat in Category A, B and Category C areas. The numeric labels on the essential habitat map can be cross referenced with the database below to determine which essential habitat factors might exist for a particular species. Essential habitat is compiled from a combination of species habitat models and buffered species records. The Department of Natural Resources, Mines and Energy website (http://www.dnrme.qld.gov.au) has more information on how the layer is applied under the State Development Assessment Provisions - State Code 16: Native vegetation clearing and the Vegetation Management Act 1999. Regional ecosystem is a mandatory essential habitat factor, unless otherwise stated. Essential habitat, for protected wildlife, means a category A area, a category B area or category C area shown on the regulated vegetation management map- 1) that has at least 3 essential habitat factors for the protected wildlife that must include any essential habitat factors that are stated as mandatory for the protected wildlife in the essential habitat database; or 2) in which the protected wildlife, at any stage of its life cycle, is located.

Protected wildlife includes endangered, vulnerable or near-threatened native wildlife prescribed under the Nature Conservation Act 1992.

Essential habitat in Category A and/or Category B and/or Category C

Label Scientific Name Common Name NCA Status Vegetation Community Altitude Soils Position in Landscape

1843 Numenius eastern curlew E Foraging on soft, intertidal mudflat, with a preference for broad Sea level to 100m. Sand, sandy mud Associated with madagascariensis flats, often in sheltered areas near mangroves and and mud coastlines and estuaries/creeks, also on sandflats and occasionally ocean substrates. wetlands. beaches, rock platforms and coral reefs. Roost on saltflat, saltmarsh, mangroves, reef flat, sandy spits and grassland near water.

Label Regional Ecosystem (mandatory unless otherwise specified)

1843 2.1.1, 2.1.2, 2.1.3, 2.1.4, 2.1.5, 3.1.1, 3.1.2, 3.1.3, 3.1.4, 3.1.5, 3.1.6, 7.1.1, 7.1.2, 7.1.3, 8.1.1, 8.1.2, 8.1.3, 8.1.4, 11.1.1, 11.1.2, 11.1.3, 11.1.4, 12.1.2, 12.1.3

Page 3 Map requested: 18/06/2019 10:53:56 Centred on: Lot: 1 Plan: RP90590

Page 1 Map requested: 18/06/2019 10:53:56 Centred on: Lot: 1 Plan: RP90590

Page 2

APPENDIX 4

Matters of Local Environmental Significance Mapping Red-e-map Print http://gis.redland.qld.gov.au/redemap/printGeneric.aspx?Title=Red-e-...

Red-e-map Plot Legend Land Current Land Current Lot Suburbs Suburb Boundary Redland City and Surrounds Redland City LGA Adjoining LGA Moreton Bay Environmental RCC Koala Habitat RE Remnant Koala Habitat RE Regrowth Koala Habitat Urban Koala Habitat Trees Urban Non Koala Habitat City Plan Version 2 Waterway Corridors and Wetlands Overlay

Precinct Boundary Precinct Boundary

Zones Low Density Residential Low-medium Density Residential Medium Density Residential Character Residential Tourist Accomodation Principal Centre Major Centre District Centre Local Centre Neighbourhood Centre Specialised Centre Recreation and Open Space Environmental Management Conservation Low Impact Industry Medium Impact Indus try Waterfront and Marine Industry Community Facilities Emerging Communities Mixed Use Rural

Scale: Date: 1:2266 19/06/2019

INFORMATION PURPOSES ONLY

No w arranty given in relation to the data (including accuracy, reliability, completeness or suitability) and no liability accepted (including w ithout limitation, liability in negligence) for any loss, damage or costs (including consequential damage) relating to any use of the data. Data must not be used for direct marketing or be used on breach of the privacy law s. External contributors to data listed at w w w .nrme.qld.gov.au/products or w w w.redland.qld.gov.au

1 of 1 19/06/2019, 11:17 am APPENDIX 5

Recorded Trees >100mm DBH APPENDIX 5 – Recorded trees >100mm DBH Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

Trees >100 mm DBH within the Stage 2 development footprint and within 10 m of the development area boundary.

Point Species Count Point Species Count 1 Tipuana tipu 1 55 Casuarina glauca 1 2 Tipuana tipu 1 56 Casuarina glauca 1 3 Tipuana tipu 1 57 Casuarina glauca 1 4 Tipuana tipu 1 58 Casuarina glauca 1 5 Mango 1 59 Casuarina glauca 1 6 Macaranga tanarius 1 60 Casuarina glauca 1 7 Macaranga tanarius 1 61 Casuarina glauca 1 8 Melaleuca quinquenervia 3 62 Casuarina glauca 1 9 Palm 1 63 Casuarina glauca 1 10 Melaleuca quinquenervia 1 64 Casuarina glauca 1 11 Melaleuca quinquenervia 1 65 Casuarina glauca 1 12 Macaranga tanarius 1 66 Casuarina glauca 1 13 Macaranga tanarius 2 67 Casuarina glauca 1 14 Melaleuca quinquenervia 1 68 Casuarina glauca 1 15 Macaranga tanarius 1 69 Casuarina glauca 1 16 Macaranga tanarius 1 70 Casuarina glauca 1 17 Macaranga tanarius 3 71 Casuarina glauca 1 18 Macaranga tanarius 1 72 Casuarina glauca 1 19 Casuarina glauca 2 73 Melaleuca quinquenervia 1 20 Melaleuca quinquenervia 1 74 Melaleuca quinquenervia 1 21 Macaranga tanarius 1 76 Casuarina glauca 1 22 Melaleuca quinquenervia 1 77 Casuarina glauca 1 23 Casuarina glauca 1 78 Casuarina glauca 1 24 Casuarina glauca 1 79 Glochidion 1 25 Macaranga tanarius 1 80 Macaranga tanarius 1 26 Macaranga tanarius 1 81 Casuarina glauca 1 27 Macaranga tanarius 1 82 Casuarina glauca 1 28 Macaranga tanarius 1 83 Casuarina glauca 1 29 Casuarina glauca 1 84 Casuarina glauca 1 30 Macaranga tanarius 1 85 Casuarina glauca 1 31 Casuarina glauca 1 86 Casuarina glauca 1 32 Casuarina glauca 1 87 Macaranga tanarius 1 33 Casuarina glauca 1 88 Casuarina glauca 1 34 Casuarina glauca 2 89 Casuarina glauca 1 35 Macaranga tanarius 1 90 Casuarina glauca 1 36 Casuarina glauca 1 91 Casuarina glauca 1 37 Casuarina glauca 1 92 Casuarina glauca 1 38 Macaranga tanarius 1 93 Casuarina glauca 1 39 Glochidion 1 94 Casuarina glauca 1 40 Melaleuca quinquenervia 1 95 Macaranga tanarius 2 41 Casuarina glauca 1 96 Casuarina glauca 1 42 Casuarina glauca 1 97 Casuarina glauca 1 43 Casuarina glauca 1 98 Casuarina glauca 1 44 Casuarina glauca 1 99 Casuarina glauca 1 45 Casuarina glauca 1 100 Casuarina glauca 1 101 Macaranga tanarius 1 151 Casuarina glauca 1 102 Casuarina glauca 1 152 Casuarina glauca 1 103 Casuarina glauca 1 153 Casuarina glauca 1 104 Casuarina glauca 1 154 Casuarina glauca 1 105 Casuarina glauca 1 155 Casuarina glauca 1 106 Casuarina glauca 1 156 Casuarina glauca 1 107 Macaranga tanarius 1 157 Casuarina glauca 1 108 Casuarina glauca 1 158 Casuarina glauca 1 109 Casuarina glauca 1 159 Casuarina glauca 1 110 Casuarina glauca 1 160 Casuarina glauca 1 111 Casuarina glauca 1 161 Casuarina glauca 1 112 highest point mangrove 1 162 Casuarina glauca 1 APPENDIX 5 – Recorded trees >100mm DBH Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

Point Species Count Point Species Count 113 Casuarina glauca 1 163 Casuarina glauca 1 114 Casuarina glauca 1 164 Casuarina glauca 1 115 Casuarina glauca 1 165 Casuarina glauca 1 116 Casuarina glauca 1 166 Casuarina glauca 1 117 Casuarina glauca 1 167 Casuarina glauca 1 118 Casuarina glauca 1 168 Casuarina glauca 1 119 Casuarina glauca 1 169 Casuarina glauca 1 120 Casuarina glauca 1 170 Casuarina glauca 1 121 Casuarina glauca 1 171 Casuarina glauca 1 122 Casuarina glauca 1 172 Casuarina glauca 1 123 Casuarina glauca 1 173 Casuarina glauca 1 124 Casuarina glauca 1 174 Casuarina glauca 1 125 Casuarina glauca 1 175 Casuarina glauca 1 126 Casuarina glauca 1 176 Casuarina glauca 1 127 Casuarina glauca 1 177 Casuarina glauca 1 128 Casuarina glauca 1 178 Casuarina glauca 1 129 Casuarina glauca 1 179 Casuarina glauca 1 130 Casuarina glauca 1 180 Casuarina glauca 1 131 Casuarina glauca 1 181 Casuarina glauca 1 132 Casuarina glauca 1 182 Casuarina glauca 1 133 Casuarina glauca 1 183 Casuarina glauca 1 134 Casuarina glauca 1 184 Casuarina glauca 1 135 Casuarina glauca 1 185 Casuarina glauca 1 136 Casuarina glauca 1 186 Casuarina glauca 1 137 Casuarina glauca 1 187 Casuarina glauca 1 138 Casuarina glauca 1 188 Casuarina glauca 1 139 Casuarina glauca 1 189 Casuarina glauca 1 140 Casuarina glauca 1 190 Casuarina glauca 1 141 Casuarina glauca 1 191 Casuarina glauca 1 142 Casuarina glauca 1 192 Casuarina glauca 1 143 Casuarina glauca 1 193 Casuarina glauca 1 144 Casuarina glauca 1 194 Casuarina glauca 1 145 Casuarina glauca 1 195 Mangrove 1 146 Casuarina glauca 1 196 Mangrove 1 147 Casuarina glauca 1 197 Casuarina glauca 1 148 Illedgis Blue habitat 1 198 Casuarina glauca 1 149 Casuarina glauca 1 199 Casuarina glauca 1 150 Casuarina glauca 1 200 Casuarina glauca 1 201 Casuarina glauca 1 250 Casuarina glauca 1 202 Mangrove 1 251 Casuarina glauca 1 203 Mangrove 1 252 Casuarina glauca 1 204 Casuarina glauca 1 253 Casuarina glauca 1 205 Casuarina glauca 1 254 Casuarina glauca 1 206 Casuarina glauca 1 255 Casuarina glauca 1 207 Casuarina glauca 1 256 Casuarina glauca 1 208 Casuarina glauca 1 257 Casuarina glauca 1 209 Casuarina glauca 1 258 Casuarina glauca 1 210 Casuarina glauca 1 259 Casuarina glauca 1 211 Casuarina glauca 1 260 Casuarina glauca 1 212 Melaleuca quinquenervia 1 261 Casuarina glauca 1 213 Melaleuca quinquenervia 1 262 Casuarina glauca 1 214 Casuarina glauca 1 263 Casuarina glauca 1 215 Casuarina glauca 1 264 Casuarina glauca 1 216 Melaleuca quinquenervia 1 265 Casuarina glauca 1 217 Eucalyptus tereticornis 1 266 Casuarina glauca 1 218 Eucalyptus tereticornis 1 267 Casuarina glauca 1 219 Eucalyptus tereticornis 1 268 Casuarina glauca 1 220 Melaleuca quinquenervia 1 269 Casuarina glauca 1 221 Eucalyptus tereticornis 1 270 Casuarina glauca 1 222 Eucalyptus tereticornis 1 271 Casuarina glauca 1 223 Eucalyptus tereticornis 1 272 Casuarina glauca 1 APPENDIX 5 – Recorded trees >100mm DBH Ecological Assessment Stage 2 Weinam Creek PDA for Redland Investment Corporation

Point Species Count Point Species Count 224 Eucalyptus tereticornis 1 273 Casuarina glauca 1 225 Eucalyptus tereticornis 1 274 Casuarina glauca 1 226 Eucalyptus tereticornis 1 275 Casuarina glauca 1 227 Eucalyptus tereticornis 1 276 Casuarina glauca 1 228 Eucalyptus tereticornis 1 277 Casuarina glauca 1 229 Eucalyptus tereticornis 1 278 Casuarina glauca 1 279 Casuarina glauca 1 1 280 Casuarina glauca 1 1 281 Casuarina glauca 1 1 282 Casuarina glauca 1 1 283 Casuarina glauca 1 1 284 Casuarina glauca 1 1 285 Casuarina glauca 1 1 286 Casuarina glauca 1 1 287 Casuarina glauca 1 1 288 Casuarina glauca 1 1 289 Eucalyptus tereticornis 1 1 290 Eucalyptus tereticornis 1 1 291 Eucalyptus tereticornis 1 1 292 Grevillea robusta 1 1 293 Grevillea robusta 1 1 294 Grevillea robusta 1 1 295 Eucalyptus tereticornis 1 1 296 Eucalyptus tereticornis 1 1 297 Eucalyptus tereticornis 1 1 298 Eucalyptus tereticornis 1 1 299 Eucalyptus tereticornis 1 300 Eucalyptus tereticornis 1 301 Acacia disparrima 1 302 Eucalyptus tereticornis 1 303 Acacia disparrima 1 304 Acacia disparrima 1 305 Acacia disparrima 1 306 Acacia disparrima 1 307 Macaranga tanarius 1 308 Eucalyptus tereticornis 1 309 Eucalyptus tereticornis 1 310 Eucalyptus tereticornis 1 311 Eucalyptus tereticornis 1 312 Eucalyptus tereticornis 1 313 Eucalyptus tereticornis 1 314 Eucalyptus tereticornis 1 315 Eucalyptus tereticornis 1 316 Eucalyptus tereticornis 1 317 Eucalyptus tereticornis 1 318 Eucalyptus tereticornis 1 319 Eucalyptus tereticornis 1 320 Eucalyptus tereticornis 1 321 Casuarina glauca 1 322 Casuarina glauca 1